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		<location><![CDATA[Culemborg, Geldermalsen, Neerrijnen]]></location>
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		<location><![CDATA[Wijdemeren]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<location><![CDATA[Barneveld, Apeldoorn]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Ommen]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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meervleermuis (Myotis dasycneme) en de rosse vleermuis (Nyctalus noctula
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Oisterwijk]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<location><![CDATA[Nieuwkoop]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Velp]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Utrecht]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<activity code="123">Destruction of breeding sites</activity>
			<activity code="124">Destruction of resting places</activity>
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		<reasons>
			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Hof van Twente]]></location>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<activities>
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			<activity code="124">Destruction of resting places</activity>
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		<reasons>
			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Oude IJsselstreek]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Castricum]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<activity code="130">Transport</activity>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Hengelo]]></location>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="Rana arvalis" userIdentity="Alterra1" derogation_reference="Alterra1-H-98-2009110610354591">
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[’s Gravenland]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<activities>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
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		<comments></comments>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2007/0472" userIdentity="Alterra1" derogation_reference="Alterra1-H-100-2009110610542339">
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		<populationSize>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2007/0477" userIdentity="Alterra1" derogation_reference="Alterra1-H-101-2009110611170854">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<location><![CDATA[Rheden en Rozendaal]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<location><![CDATA[Sneek]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<populationSize>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Alkmaar]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Eindhoven]]></location>
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			<activity code="123">Destruction of breeding sites</activity>
			<activity code="124">Destruction of resting places</activity>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
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		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Nijmegen]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<populationSize>
			<individuals>0</individuals>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[IJsselmuiden]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2007/0441" userIdentity="Alterra1" derogation_reference="Alterra1-H-157-2009111913571555">
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Amsterdam]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<activity code="124">Destruction of resting places</activity>
			<activity code="130">Transport</activity>
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		</methods>
		<reasons>
			<reason code="15">For other imperative reasons of overriding public interest, including those of beneficial consequences of primary importance for the environment</reason>
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			<individuals>0</individuals>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Roermond]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2007/0447" userIdentity="Alterra1" derogation_reference="Alterra1-H-159-2009111914210570">
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		<species><![CDATA[Pipistrellus pipistrellus]]></species>
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		<alternativesAssessed></alternativesAssessed>
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			<activity code="123">Destruction of breeding sites</activity>
			<activity code="124">Destruction of resting places</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Haarlemmermeer]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<activity code="124">Destruction of resting places</activity>
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		<methods>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
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		<populationSize>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Renkum]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<alternativesAssessed></alternativesAssessed>
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			<activity code="124">Destruction of resting places</activity>
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		<methods>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
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		<derogationJustification></derogationJustification>
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		<populationSize>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Bergeijk]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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			<activity code="123">Destruction of breeding sites</activity>
			<activity code="124">Destruction of resting places</activity>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Terneuzen]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<alternativesAssessed></alternativesAssessed>
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			<activity code="124">Destruction of resting places</activity>
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		<methods>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Enschede]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<activity code="123">Destruction of breeding sites</activity>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Heerhugowaard]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<alternativesAssessed></alternativesAssessed>
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		<methods>
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		<reasons>
			<reason code="15">For other imperative reasons of overriding public interest, including those of beneficial consequences of primary importance for the environment</reason>
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		<populationSize>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Soest]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2008/0052" userIdentity="Alterra1" derogation_reference="Alterra1-H-166-2009111915063878">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<species><![CDATA[Rana lessonea, Bufo calamita]]></species>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Utrechtse Heuvelrug]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Alphen aan de Rijn, Bodegraven]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<comments></comments>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<methods>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
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		<sensitive>false</sensitive>
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		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Aa en Hunze]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<comments></comments>
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		<populationSize>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Heusden]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<comments></comments>
		<location><![CDATA[Zwolle, Hattem, Kampen, Dronten, Lelystad]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<comments></comments>
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		<populationSize>
			<individuals>0</individuals>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Deventer]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2008/0041" userIdentity="Alterra1" derogation_reference="Alterra1-H-205-2009112411113238">
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Noordwijk, Katwijk, Wassenaar]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Dordrecht]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<species><![CDATA[Triturus cristatus, Rana lessonae, Bufo calamita, Nyctalus leisleri, Pipistrellus pipistrellus, Plecotus auritus, Eptesicus serotinus, Nyctalus noctula, Pipistrellus nathusii, Myotis daubentonii]]></species>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<activities>
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			<reason code="15">For other imperative reasons of overriding public interest, including those of beneficial consequences of primary importance for the environment</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Uithoorn]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<sensitive>false</sensitive>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Waalre]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<activities>
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		<sensitive>false</sensitive>
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		<alternativesAssessed></alternativesAssessed>
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			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Noordoostpolder]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Boarnsterhim]]></location>
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			<activity code="124">Destruction of resting places</activity>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Wijchen]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<activity code="124">Destruction of resting places</activity>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Amsterdam]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Zaltbommel]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Bunnik]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<reasons>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Hoogezand-Sappemeer]]></location>
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		<alternativesAssessed></alternativesAssessed>
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			<otherType></otherType>
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		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Moerdijk]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2008/0107" userIdentity="Alterra1" derogation_reference="Alterra1-H-234-2009112515094781">
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Ommen]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Noordoostpolder]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/268" user_derogation_ref="FF/75C/2008/0189" userIdentity="Alterra1" derogation_reference="Alterra1-H-237-2009112515291154">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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			<reason code="15">For other imperative reasons of overriding public interest, including those of beneficial consequences of primary importance for the environment</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
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		<populationSize>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Rijnwoude]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Assen]]></location>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Groningen]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Haarlem]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Wymbritseradiel]]></location>
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		<reasons>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<reasons>
			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Hoek van Holland]]></location>
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		<species><![CDATA[Rana lessonae]]></species>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<comments></comments>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Oost-Gelre]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<comments></comments>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<activity code="121">Deterioration of breeding sites</activity>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Sint Anthonis,  Wanrooij]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<location><![CDATA[Nijkerk]]></location>
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		<sensitive>false</sensitive>
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		<location><![CDATA[Ooststellingwerf]]></location>
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		<species><![CDATA[Bufo calamita]]></species>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Beemster]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Wageningen]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Zevenaar]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Son en Breugel]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Ouderkerk aan den IJssel]]></location>
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		<sensitive>false</sensitive>
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		<location><![CDATA[Mill, Escharen]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Den Haag]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Leek]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<activity code="123">Destruction of breeding sites</activity>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<comments></comments>
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		<reasons>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<location><![CDATA[Scherpenzeel]]></location>
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		<reasons>
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		<location><![CDATA[Enschede]]></location>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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		<sensitive>false</sensitive>
		<comments></comments>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<sensitive>false</sensitive>
		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Lunteren]]></location>
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		<location><![CDATA[Olst Wijhe]]></location>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Moerdijk]]></location>
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		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Culemborg]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<alternativesAssessed></alternativesAssessed>
		<activities>
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			<activity code="123">Destruction of breeding sites</activity>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Boekel]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<comments></comments>
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		<comments></comments>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
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			<activity code="121">Deterioration of breeding sites</activity>
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			<activity code="124">Destruction of resting places</activity>
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			<reason code="13">For other imperative reasons of overriding public interest, including those of a social nature</reason>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Leeuwarden]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<sensitive>false</sensitive>
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			<activity code="124">Destruction of resting places</activity>
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			<activity code="124">Destruction of resting places</activity>
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		<sensitive>false</sensitive>
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		<location><![CDATA[Achtkarspelen]]></location>
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			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<comments></comments>
		<location><![CDATA[Geldermalsen]]></location>
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			<activity code="123">Destruction of breeding sites</activity>
			<activity code="124">Destruction of resting places</activity>
			<activity code="130">Transport</activity>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments></comments>
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			<activity code="124">Destruction of resting places</activity>
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		<methods>
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		<reasons>
			<reason code="14">For other imperative reasons of overriding public interest, including those of an economic nature</reason>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[None]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Ede]]></location>
		<licensedJustification><![CDATA[Not provided]]></licensedJustification>
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		<species><![CDATA[Tyto alba]]></species>
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			<region code="NL42">Limburg (NL)</region>
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		<alternativesAssessed><![CDATA[Er zijn verschillende alternatieven onderzocht voor de locatie en inrichting van het Trade Port Noord, Park Zaarderheiken en Floriade/Greenport. Deze zijn beschreven in de diverse bestemmingsplannen ‘Bestemmingsplan Bedrijvenpark Trade Port Noord’ (2004), ‘Bestemmingsplan Bedrijventerrein Trade Port Noord en park Zaarderheiken’ (2006) en het ‘Bestemmingsplan Floriade/Greenport’ (2007). Alle bestemmingsplannen gaan grotendeels uit van de MER die in 1998 is opgesteld voor het gebied Venlo Noord-West.
In het MMA (Meest Milieuvriendelijk Alternatief) is aangegeven dat het zuidelijke gebied in de oksel van het knooppunt van de A67 met de A73 dient te worden ontzien vanwege de hoge natuurwaarden. Dit wordt in de diverse bestemmingsplannen grotendeels aangehouden, afgezien op enkele punten. Voor de golfbaan Park Zaarderheiken is een MER opgesteld, die de effecten op soorten en ontwikkelingsmogelijkheden mee heeft genomen om het MMA te bepalen. In de MER voor de Floriade 2012 is voornamelijk gekeken naar alternatieven voor het herbergen van het miljoenenpubliek en het verwerken van het vele verkeer.
Hoewel de bestemmingsplannen en de MER’s relatief globaal zijn opgesteld en niet tot op soortniveau doordringen, zijn naar mijn mening in de opgestelde plannen wel de meest waardevolle gebieden ontzien door de gemaakte keuzes in alternatieven. Hierdoor worden met betrekking tot vele beschermde soorten geen verbodsbepalingen overtreden en wordt schade zoveel mogelijk voorkomen. Een eerder voorgesteld alternatief voor de compensatie voor de kerkuil en de steenuil was geen optie, omdat het gelegen is in een gebied waar, in de nabije toekomst, een nieuwe bestemming wordt opgelegd ten nadele van het voortbestaan van de compensatie. Het project, waarvoor ontheffing wordt aangevraagd, is wel probleemoplossend. De nu geplande compensatie voor kerkuil en steenuil kan voor een langere periode duurzaam behouden worden.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
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		<selectiveBasis></selectiveBasis>
		<licensed>
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			<eggs>0</eggs>
			<nests>3</nests>
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			<eggs>0</eggs>
			<nests>3</nests>
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			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
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		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Ten minste twee weken vóór het verwijderen van de huidige broedlocaties van de kerkuil en de steenuil, dient per soort en per te verwijderen nestgelegenheid één nestkast te worden opgehangen binnen de territoria van de uilen, maar buiten de invloedssfeer van Trade Port Noord.
8. Bij het ophangen van nestkasten voor de steenuil dienen de volgende voorwaarden gevolgd te worden:
a. De nestkasten dienen te zijn voorzien van een ‘anti-kauwensluis’. Ook dient nestmateriaal (hooi, bladeren of takjes) in de kasten gelegd te worden.
b. Nestkasten dienen zodanig te worden geplaatst dat deze nimmer in het volle zonlicht komen te staan; bij de plaatsing van een nestkast aan en/of in een gebouw, dient een schaduwrijke, noordelijk gerichte gevel te worden gekozen.
c. De nestkasten dienen op rustige locaties te hangen, met voldoende dekking. De nestkasten dienen 2 tot 4 meter boven het maaiveld te worden geplaatst.
d. De nestkasten dienen zodanig te worden geplaatst dat de uilen bij het af- en aanvliegen geen weg moeten passeren, om verkeersslachtoffers te voorkomen. Ook dienen de kasten niet boven water gehangen te worden, om mogelijke verdrinking van nog niet vliegvlugge jongen te voorkomen.
9. Bij het ophangen van nestkasten voor de kerkuil dienen de volgende voorwaarden gevolgd te worden:
a. De nestkasten voor de kerkuil dienen geplaatst te worden op de zolder of in de nok van een gebouw of schuur met een opening voor de kerkuil.
b. De nestkasten dienen te zijn voorzien van een ‘anti-kauwensluis’ of inlooppijp.
10. Het verwijderen van de huidige broedlocatie wordt alleen toegestaan, indien de locatie niet in gebruik is als broedlocatie en vóór aanvang van de eerstvolgende balts- en broedperiode.
11. De plaatsing van nestkasten en het verwijderen van de huidige broedlocatie dienen te worden uitgevoerd na raadpleging en onder begeleiding van een ter zake kundige1.
12. Voorafgaand aan het aantasten van leefgebied van de steenuil en kerkuil, dient de in totaal 9,9 ha compensatie binnen het plangebied te zijn ingericht en beheerd.
13. De overige 13,8 ha compensatiegebieden ten zuiden van de A67 als is aangegeven in figuur 2 van de brief van de gemeente Venlo met kenmerk BLSON/2007/3747, d.d. 3 oktober 2007, dienen vóór het verstrijken van de geldigheidstermijn van deze ontheffing te zijn ingericht en beheerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project ‘Uitbreiding bedrijventerrein Trade Port Noord, Park Zaarderheiken, Businesspark Venlo en Floriade’ in de gemeente Venlo]]></location>
		<licensedJustification><![CDATA[Door de voorgenomen maatregelen zullen de volgende uilennesten verdwijnen:
·  Eén in 2005 voor het laatst gebruikte nestkast van een kerkuil en een in gebruik zijnde roestplaats van een steenuil in de grote schuur bij Heierhoeve;
·  Eén in 2006 gebruikte nestkast van een kerkuil in een paardenstal;
·  In de schuur op locatie (205,1x379,9) ten westen van de Annahoeve]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2006/0454" userIdentity="Alterra1" derogation_reference="Alterra1-B-22-2009121417230495">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-01-16</licenseValidFrom>
		<licenseValidUntil>2012-06-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Er zijn verschillende alternatieven onderzocht voor de locatie en inrichting van het Trade Port Noord, Park Zaarderheiken en Floriade/Greenport. Deze zijn beschreven in de diverse bestemmingsplannen ‘Bestemmingsplan Bedrijvenpark Trade Port Noord’ (2004), ‘Bestemmingsplan Bedrijventerrein Trade Port Noord en park Zaarderheiken’ (2006) en het ‘Bestemmingsplan Floriade/Greenport’ (2007). Alle bestemmingsplannen gaan grotendeels uit van de MER die in 1998 is opgesteld voor het gebied Venlo Noord-West.
In het MMA (Meest Milieuvriendelijk Alternatief) is aangegeven dat het zuidelijke gebied in de oksel van het knooppunt van de A67 met de A73 dient te worden ontzien vanwege de hoge natuurwaarden. Dit wordt in de diverse bestemmingsplannen grotendeels aangehouden, afgezien op enkele punten. Voor de golfbaan Park Zaarderheiken is een MER opgesteld, die de effecten op soorten en ontwikkelingsmogelijkheden mee heeft genomen om het MMA te bepalen. In de MER voor de Floriade 2012 is voornamelijk gekeken naar alternatieven voor het herbergen van het miljoenenpubliek en het verwerken van het vele verkeer.
Hoewel de bestemmingsplannen en de MER’s relatief globaal zijn opgesteld en niet tot op soortniveau doordringen, zijn naar mijn mening in de opgestelde plannen wel de meest waardevolle gebieden ontzien door de gemaakte keuzes in alternatieven. Hierdoor worden met betrekking tot vele beschermde soorten geen verbodsbepalingen overtreden en wordt schade zoveel mogelijk voorkomen. Een eerder voorgesteld alternatief voor de compensatie voor de kerkuil en de steenuil was geen optie, omdat het gelegen is in een gebied waar, in de nabije toekomst, een nieuwe bestemming wordt opgelegd ten nadele van het voortbestaan van de compensatie. Het project, waarvoor ontheffing wordt aangevraagd, is wel probleemoplossend. De nu geplande compensatie voor kerkuil en steenuil kan voor een langere periode duurzaam behouden worden.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
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			<eggs>0</eggs>
			<nests>2</nests>
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		<actuallyTaken>
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			<otherType></otherType>
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		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Ten minste twee weken vóór het verwijderen van de huidige broedlocaties van de kerkuil en de steenuil, dient per soort en per te verwijderen nestgelegenheid één nestkast te worden opgehangen binnen de territoria van de uilen, maar buiten de invloedssfeer van Trade Port Noord.
8. Bij het ophangen van nestkasten voor de steenuil dienen de volgende voorwaarden gevolgd te worden:
a. De nestkasten dienen te zijn voorzien van een ‘anti-kauwensluis’. Ook dient nestmateriaal (hooi, bladeren of takjes) in de kasten gelegd te worden.
b. Nestkasten dienen zodanig te worden geplaatst dat deze nimmer in het volle zonlicht komen te staan; bij de plaatsing van een nestkast aan en/of in een gebouw, dient een schaduwrijke, noordelijk gerichte gevel te worden gekozen.
c. De nestkasten dienen op rustige locaties te hangen, met voldoende dekking. De nestkasten dienen 2 tot 4 meter boven het maaiveld te worden geplaatst.
d. De nestkasten dienen zodanig te worden geplaatst dat de uilen bij het af- en aanvliegen geen weg moeten passeren, om verkeersslachtoffers te voorkomen. Ook dienen de kasten niet boven water gehangen te worden, om mogelijke verdrinking van nog niet vliegvlugge jongen te voorkomen.
9. Bij het ophangen van nestkasten voor de kerkuil dienen de volgende voorwaarden gevolgd te worden:
a. De nestkasten voor de kerkuil dienen geplaatst te worden op de zolder of in de nok van een gebouw of schuur met een opening voor de kerkuil.
b. De nestkasten dienen te zijn voorzien van een ‘anti-kauwensluis’ of inlooppijp.
10. Het verwijderen van de huidige broedlocatie wordt alleen toegestaan, indien de locatie niet in gebruik is als broedlocatie en vóór aanvang van de eerstvolgende balts- en broedperiode.
11. De plaatsing van nestkasten en het verwijderen van de huidige broedlocatie dienen te worden uitgevoerd na raadpleging en onder begeleiding van een ter zake kundige1.
12. Voorafgaand aan het aantasten van leefgebied van de steenuil en kerkuil, dient de in totaal 9,9 ha compensatie binnen het plangebied te zijn ingericht en beheerd.
13. De overige 13,8 ha compensatiegebieden ten zuiden van de A67 als is aangegeven in figuur 2 van de brief van de gemeente Venlo met kenmerk BLSON/2007/3747, d.d. 3 oktober 2007, dienen vóór het verstrijken van de geldigheidstermijn van deze ontheffing te zijn ingericht en beheerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project ‘Uitbreiding bedrijventerrein Trade Port Noord, Park Zaarderheiken, Businesspark Venlo en Floriade’ in de gemeente Venlo]]></location>
		<licensedJustification><![CDATA[Door de voorgenomen maatregelen zullen de volgende uilennesten verdwijnen:
·  Eén in 2005 voor het laatst gebruikte nestkast van een kerkuil en een in gebruik zijnde roestplaats van een steenuil in de grote schuur bij Heierhoeve;
·  Eén in 2006 gebruikte nestkast van een kerkuil in een paardenstal;
·  In de schuur op locatie (205,1x379,9) ten westen van de Annahoeve]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0103A" userIdentity="Alterra1" derogation_reference="Alterra1-B-23-2009121417263984">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-01-22</licenseValidFrom>
		<licenseValidUntil>2012-08-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL31">Utrecht</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">verwijderen nestkast</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van groot openbaar belang en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
6. Bij de planning van de werkzaamheden dient rekening te worden gehouden met de seizoensactiviteiten van de steenuil (broedperiode) om verstoring in deze meest kwetsbare perioden te voorkomen.
13. Het ongeschikt maken of verwijderen van de vaste rust- en verblijfplaats van de steenuil dient plaats te vinden buiten de broedperiode van deze soort. Ter compensatie van de te verdwijnen broedlocatie dienen minimaal drie, specifiek voor deze soort geschikte nestkasten te worden geplaatst op een geschikte locatie. Deze nestkasten dienen duurzaam te worden onderhouden.
14. De inrichting en beheer van de natuurontwikkelingszone dienen (mede) op de steenuil te zijn afgestemd.
18. De bovengenoemde mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de betreffende soort.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[betreft het agrarisch gebied ter grootte van circa 120 hectare ten oosten van de gemeente Veenendaal, in de kilometerhokken 168-447, 168-448 en 168-449]]></location>
		<licensedJustification><![CDATA[Door de voorgenomen maatregelen zullen de volgende uilennesten verdwijnen:]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0252" userIdentity="Alterra1" derogation_reference="Alterra1-B-24-2009121417484777">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-01-25</licenseValidFrom>
		<licenseValidUntil>2012-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De gemeenten Hengelo en Borne maken volgens de Nota ruimte onderdeel uit van de Netwerkstad Twente. In de Nota ruimte wordt aangegeven dat Netwerkstad Twente aangewezen is als stedelijk netwerk van (internationale) betekenis. Een stedelijk netwerk (volgens de Nota ruimte) moet door samenwerking de ruimtelijke kwaliteit bevorderen en een hoogwaardig sociaal, economisch en cultureel vestigingsklimaat bieden. Het project Kristenbos past binnen het Streekplan Overijssel 2000+ om de regio Borne- Hengelo te versterken door de ontwikkeling van woon- en werkgebieden (Vinex locatie). Het regionale beleid is verankerd in de Vinex- afspraken en de Intentieafspraken voor de verstedelijking in Twente voor de periode 2005-2010. Daarnaast is het ruimtelijk beleid voor Hengelo en is opgenomen in de Stadsvisie 2010 die met het rijk en de provincie is opgesteld. Bij de locatieafweging van het Kristenbos zijn de geplande en reeds gerealiseerde ontwikkeling van de aangrenzende woongebieden van Hengelo en Borne leidend geweest. In verhouding met andere uitbreidingslocaties is verstoring van natuurwaarden in Kristenbos volgens u het meest aanvaardbaar geacht. Bij de inrichting is alleen een afweging gemaakt of het inpassen van het bos mogelijk was. De afweging die hierbij is gemaakt is aanvaardbaar, maar niet alle soorten hebben hier profijt van. Echter met de ontheffing gestelde voorwaarden, wordt op een zodanige gewerkt dat schade aan populaties zo veel mogelijk voorkomen wordt. Het is aangetoond dat bij de inrichting zodanig met de aanwezige soorten rekening is gehouden dat het project op deze manier uitgevoerd kan worden.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">verwijderen nestkast</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van groot openbaar belang en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
9. De sloop van de huidige bebouwing dient buiten de periode augustus-september uitgevoerd te worden.
10. De vijf nestkasten voor de steenuil dienen vóór het begin van de werkzaamheden aan de rand van het plangebied geplaatst te worden. Het nest van de steenuil dient pas verwijderd te worden als zeker is dat de jongen zijn uitgevlogen.
11. Het plaatsen van de steenuilenkasten dient te gebeuren onder leiding van een ter zake kundige1 op het gebied van steenuilen.
12. Het landschap direct ten noorden van het plangebied dient geschikt te worden gemaakt voor de steenuil door middel van aanleg van landschapselementen en het creëren van groene weiden met daarnaast voldoende geschikte zitplaatsen en schuilmogelijkheden aanwezig. Hiervan dient een inrichtingsplan ter kennisname naar Dienst Regelingen gestuurd te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Kristenbos"in de gemeente Hengelo.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0252" userIdentity="Alterra1" derogation_reference="Alterra1-B-25-2009121500322175">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-01-25</licenseValidFrom>
		<licenseValidUntil>2012-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Strix aluco]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De gemeenten Hengelo en Borne maken volgens de Nota ruimte onderdeel uit van de Netwerkstad Twente. In de Nota ruimte wordt aangegeven dat Netwerkstad Twente aangewezen is als stedelijk netwerk van (internationale) betekenis. Een stedelijk netwerk (volgens de Nota ruimte) moet door samenwerking de ruimtelijke kwaliteit bevorderen en een hoogwaardig sociaal, economisch en cultureel vestigingsklimaat bieden. Het project Kristenbos past binnen het Streekplan Overijssel 2000+ om de regio Borne- Hengelo te versterken door de ontwikkeling van woon- en werkgebieden (Vinex locatie). Het regionale beleid is verankerd in de Vinex- afspraken en de Intentieafspraken voor de verstedelijking in Twente voor de periode 2005-2010. Daarnaast is het ruimtelijk beleid voor Hengelo en is opgenomen in de Stadsvisie 2010 die met het rijk en de provincie is opgesteld. Bij de locatieafweging van het Kristenbos zijn de geplande en reeds gerealiseerde ontwikkeling van de aangrenzende woongebieden van Hengelo en Borne leidend geweest. In verhouding met andere uitbreidingslocaties is verstoring van natuurwaarden in Kristenbos volgens u het meest aanvaardbaar geacht. Bij de inrichting is alleen een afweging gemaakt of het inpassen van het bos mogelijk was. De afweging die hierbij is gemaakt is aanvaardbaar, maar niet alle soorten hebben hier profijt van. Echter met de ontheffing gestelde voorwaarden, wordt op een zodanige gewerkt dat schade aan populaties zo veel mogelijk voorkomen wordt. Het is aangetoond dat bij de inrichting zodanig met de aanwezige soorten rekening is gehouden dat het project op deze manier uitgevoerd kan worden.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">verwijderen nestkast</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van groot openbaar belang en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
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			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
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		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
13. In het bosperceel ten noorden van Kristenbos dienen twee nestkasten voor de bosuil geplaatst te worden.
14. Aanplant van bos aan de noordrand van Hengelo is noodzakelijk om zo het leefgebied van bosuil en sperwer voor de lange termijn te versterken.
15. Werkzaamheden aan het bos dienen plaats te vinden in de periode september-oktober.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Kristenbos"in de gemeente Hengelo.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0252" userIdentity="Alterra1" derogation_reference="Alterra1-B-26-2009121500353562">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-01-25</licenseValidFrom>
		<licenseValidUntil>2012-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Accipiter nisus]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De gemeenten Hengelo en Borne maken volgens de Nota ruimte onderdeel uit van de Netwerkstad Twente. In de Nota ruimte wordt aangegeven dat Netwerkstad Twente aangewezen is als stedelijk netwerk van (internationale) betekenis. Een stedelijk netwerk (volgens de Nota ruimte) moet door samenwerking de ruimtelijke kwaliteit bevorderen en een hoogwaardig sociaal, economisch en cultureel vestigingsklimaat bieden. Het project Kristenbos past binnen het Streekplan Overijssel 2000+ om de regio Borne- Hengelo te versterken door de ontwikkeling van woon- en werkgebieden (Vinex locatie). Het regionale beleid is verankerd in de Vinex- afspraken en de Intentieafspraken voor de verstedelijking in Twente voor de periode 2005-2010. Daarnaast is het ruimtelijk beleid voor Hengelo en is opgenomen in de Stadsvisie 2010 die met het rijk en de provincie is opgesteld. Bij de locatieafweging van het Kristenbos zijn de geplande en reeds gerealiseerde ontwikkeling van de aangrenzende woongebieden van Hengelo en Borne leidend geweest. In verhouding met andere uitbreidingslocaties is verstoring van natuurwaarden in Kristenbos volgens u het meest aanvaardbaar geacht. Bij de inrichting is alleen een afweging gemaakt of het inpassen van het bos mogelijk was. De afweging die hierbij is gemaakt is aanvaardbaar, maar niet alle soorten hebben hier profijt van. Echter met de ontheffing gestelde voorwaarden, wordt op een zodanige gewerkt dat schade aan populaties zo veel mogelijk voorkomen wordt. Het is aangetoond dat bij de inrichting zodanig met de aanwezige soorten rekening is gehouden dat het project op deze manier uitgevoerd kan worden.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">verwijderen nestkast</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van groot openbaar belang en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
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			<individuals>0</individuals>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
13. In het bosperceel ten noorden van Kristenbos dienen twee nestkasten voor de bosuil geplaatst te worden.
14. Aanplant van bos aan de noordrand van Hengelo is noodzakelijk om zo het leefgebied van bosuil en sperwer voor de lange termijn te versterken.
15. Werkzaamheden aan het bos dienen plaats te vinden in de periode september-oktober.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Kristenbos"in de gemeente Hengelo.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0253" userIdentity="Alterra1" derogation_reference="Alterra1-B-27-2009121516203240">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-01-25</licenseValidFrom>
		<licenseValidUntil>2012-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Picus viridis, Tyto alba, Falco tinnunculus]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project Dalmeden moet zorgen voor een overgang van de stad naar het landelijk gebied.
Daarom wordt een groot gedeelte van het oppervlak niet bebouwd. Het project komt voort uit de “Ruimte voor ruimte” regeling die in 2000 door de regering is vastgesteld.
In 2001 is voor de realisatie hiervan Bestuursovereenkomst tot stand gekomen tussen u en de Provincie Overijssel. De hierin gemaakte afspraken zijn verder uitgewerkt in de bij de aanvraag gevoegde “Nota van Uitgangspunten”. Aan de gebiedskeuze voor realisatie van “Ruimte voor ruimte” (RvR) woningen in het plangebied Dalmeden heeft u een aantal afwegingen gemaakt. Ten eerste is provinciaal de keuze gemaakt om RvRwoningen te realiseren door clustering in stedelijke vorm in plaats van verspreid over het gebied. Doel hierbij is het landelijke gebied te ontzien en het mogelijk maken van ruim opgezette woningbouw aan de stadsrand. Tegelijkertijd verlangt de Provincie dat de nadruk moet komen te liggen op het landelijk wonen in een sterk landschapsontwerp van de aan te wijzen woongebieden. Binnen de noordflank komen als alternatieve locaties alleen direct aangrenzende gebieden in aanmerking. De keuze daarin is beperkt door de gemeentegrens en de belangrijke landschappelijke waarden van het nabijgelegen beekdal van de Deurningerbeek. Bij de keuze voor Dalmeden zijn landschap en bereikbaarheid de belangrijkste afwegingskaders geweest. Het gebied Dalmeden bestaat uit een relatief open landschap met weilanden en akkerbouw. De alternatieven scoren niet gunstiger ten aanzien van de voor het gebied kenmerkende natuurwaarden. De inrichting van Dalmeden hangt sterk af van de hydrologische situatie in het gebied. Doordat het plangebied in een beekdal ligt is het noodzakelijk dat in het gebied grote open ruimtes aanwezig zijn, als overstroming- en inundatiegebied. De ruime stedenbouwkundige opzet biedt de mogelijkheid van een verkaveling voor vrijstaand wonen met een landelijk karakter. Op deze manier wordt er een landschappelijke afronding gecreëerd van de stadsrand waardoor intensieve verstedelijking aan de noordrand wordt voorkomen. Dit wordt versterkt doordat het buitengebied rondom Dalmeden landschappelijk wordt opgewaardeerd. Hierdoor blijft een gedeelte van het gebied in stand als leefgebied voor de aanwezige soorten, daarnaast zal het gebied rondom Dalmeden versterkt worden met landschapselementen.
Tevens vindt er compensatie plaats voor het leefgebied van de heikikker. De maatregelen die genomen zijn zorgen ervoor dat de gunstige staat van instandhouding van de aanwezige soorten niet in het geding is. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd, groene specht, kerkuil en de torenvalk komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[het project “Dalmeden” in de gemeente Hengelo]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0318" userIdentity="Alterra1" derogation_reference="Alterra1-B-28-2009122414564688">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-02-06</licenseValidFrom>
		<licenseValidUntil>2012-09-15</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[De gekozen locatie is volgens u speciaal aangewezen door de provincie voor het vestigen van het nieuwe gemeentehuis van de gemeente Bronckhorst. Het landschapsplan (gemaakt door bureau Schokland en Water) stelt tevens een zevental voorwaarden voor de ligging van het gemeentehuis. Bij de huidige keuze is rekening gehouden met: archeologie, geomorfologie, bodem, verkeerskundige ontsluiting, parkeren, water, milieu en ecologie.
Gebieden waar ecologie geen enkele rol speelt, zijn niet voorhanden. De kans is inderdaad groot dat er op andere locaties ook steenuilen aanwezig zijn. Er is voldoende aangetoond dat ecologisch gezien er geen mogelijkheid bestaat tot inpassing van de huidige elementen in het project. De mitigerende en compenserende maatregelen die door u worden voorgesteld, zorgen er echter wel voor dat de beschermde soort van het gebied gebruik kan blijven maken. Na de werkzaamheden zal het perceel nog steeds geschikt zijn als rust- en foerageergebied voor deze soort. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
Sp
7. De compenserende en mitigerende maatregelen dienen te worden uitgevoerd zoals beschreven in hoofdstuk 4 en 6 van het bij de aanvullende gegevens van 14 november 2007 gevoegde rapport “Aanvulling ontheffingsaanvraag, Behorend bij de ontheffingsaanvraag flora en faunawet FF/75C/2007/0318 voor de bouw van het nieuwe gemeentehuis van de gemeente Bronckhorst” van 10 november 2007.
8. Er worden, voorafgaand aan het amoveren van bebouwing en beplanting, vijf nestkasten met marterbeveiliging opgehangen in de directe omgeving door de heer Stoltenborg.
9. Er worden 10 wilgen (waarvan 5 volwassen holle bomen), 5 elzen, 9 fruitbomen geplant in het noordelijke deel, voorafgaand aan het amoveren van bebouwing en beplanting. De maten van de te beplante bomen staan beschreven in de tabellen op bladzijde 7 van Foreest Groen Consult, 2008.
10. De van elders te verwijderen volwassen holle bomen om deze op de planlocatie te plaatsen, dienen, voorafgaand aan het verwijderen van deze bomen, onderzocht te worden door een ter zake kundige1 op hun eventuele functie voor beschermde soorten (steenuil, maar bijvoorbeeld ook vleermuizen) op hun huidige locatie.
11. Alle bomen en beplantingselementen worden, voorafgaand aan het amoveren van bebouwing en beplanting, met behulp van stevige rasters ruim uitgerasterd. De rastermaten staan beschreven in de tabel op bladzijde 7 van Foreest Groen Consult, 2008).
12. Tijdens de sloop dient een ter zake kundige1 op het gebied van steenuilen aanwezig te zijn, die de bebouwing en beplanting voor de sloop controleert op eventuele aanwezigheid van steenuilen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[Elderinkweg 2, Hengelo]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2006/0343" userIdentity="Alterra1" derogation_reference="Alterra1-B-29-2009122415170975">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-22</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis,  Athene noctua]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Op grond van de provinciale en locale becijferingen is gebleken dat er in Veldhoven behoefte is aan nieuwe bedrijfsterreinen. In het Regionaal Ruimtelijk Plan zuidoost Brabant, dat opgesteld is in 2004, is opgenomen waar de komende jaren woningen en bedrijfsterreinen gerealiseerd gaan worden om te kunnen voorzien in de behoeften. Voor de aanleg van één van de bedrijventerreinen is de locatie Habraken aangewezen. Gezien de structuur van de gemeente Veldhoven en de aanwezige beperkingen die het vliegveld de gemeente oplegt (zonering), is ervoor gekozen om het bedrijfsterrein te projecteren binnen de zonering die niet voor andere doeleinden aan te wenden was. Uit een rapportage van de Vogelwerkgroep de Kempen blijkt dat rondom de hele bebouwde kom van de gemeente Veldhoven meerdere territoria van de groene specht, kerkuil en de steenuil voorkomen.
Bij de keuze voor de bouw van een nieuw bedrijfsterrein is de kans altijd aanwezig dat een territorium van één of meerdere van de genoemde soorten verkleind of vernietigd wordt. Bij de huidige locatiekeuze voor Habraken zijn de consequenties voor deze soorten gering. Met betrekking tot alternatieven in de werkwijze en de inrichting van het plangebied wordt er echter voldoende rekening gehouden met het belang van het foerageergebied voor de steenuil. Er is een compensatieplan opgesteld om de negatieve effecten van de aantasting van het foerageergebied te minimaliseren. De voorgenomen inrichtingsmaatregelen uit het compensatieplan worden zo snel mogelijk uitgevoerd, zodat de uilen zich aan de nieuwe inrichting kunnen aanpassen voordat het terrein bouwrijp wordt gemaakt. Hiermee is het voldoende aangetoond dat voor het project geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>4</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht en de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het project dient uitgevoerd te worden conform het bij de ontheffingsaanvraag gevoegde rapport ‘Compensatieplan steenuil Habraken’ van 5 februari 2008 en conform de aanbevelingen in paragraaf 3.2 van het bij de ontheffingsaanvraag gevoegde rapport ‘Aanvullend onderzoek plangebied Habraken’, 14 januari 2008.
8. Er dient een voortgangsrapportage opgesteld te worden waarin het volgende is omschreven:
1. Hoe de definitieve inrichting van het compensatiegebied eruit ziet en welke inrichtingswerkzaamheden zijn daartoe uitgevoerd.
2. Hoe het definitieve beheer van het compensatiegebied voor de steenuil is opgezet.
3. Hoe het definitieve beheer van de wegbermen in het plangebied ten behoeve van het rapunzelklokje is opgezet.
9. De voortgangsrapportage dient, voorafgaand aan de uitvoering van de werkzaamheden aan het directe leefgebied van de steenuil (uitgezonderd inrichtingswerkzaamheden aan het compensatiegebied), via Dienst Regelingen ter goedkeuring verzonden te worden naar het Ministerie van LNV. Pas nadat het Ministerie van LNV haar goedkeuring heeft gegeven, kunnen de werkzaamheden aan het directe leefgebied van de steenuil van start gaan. Het directe leefgebied van de steenuil betreft het gebied in een straal van 250 meter om de broedlocatie van de steenuil heen.
10. Na voltooiing van de inrichting van het compensatiegebied voor de steenuil dient het functioneren van het compensatiegebied gedurende de looptijd van deze ontheffing door middel van monitoring gevolgd te worden. De resultaten hiervan dienen door middel van een verslag jaarlijks vóór 31 december via Dienst Regelingen ter beoordeling voorgelegd te worden aan het Ministerie van LNV, voor het eerst in 2009. Indien de monitoringsresultaten daartoe aanleiding geven, kunnen er extra voorwaarden gesteld worden aan de ontheffing.
11. Het effectmetingverslag dat na vijf jaar wordt opgesteld, dient, via Dienst Regelingen, toegestuurd te worden aan het ministerie van LNV.
12. Alle werkzaamheden (inclusief inrichtingswerkzaamheden aan het compensatiegebied) in het directe leefgebied van de steenuil dienen kleinschalig en fasegewijs uitgevoerd te worden en dienen te worden begeleid door een ter zake kundige1. Het directe leefgebied van de steenuil betreft het gebied in een straal van 250 meter om de broedlocatie van de steenuil heen.
13. De werkzaamheden (uitgezonderd inrichtingswerkzaamheden aan het compensatiegebied) in het directe leefgebied mogen niet plaatsvinden in de broedperiode van de soort. Het directe leefgebied van de steenuil betreft het gebied in een straal van 250 meter om de broedlocatie van de steenuil heen.
14. De werkzaamheden in de omgeving van het directe leefgebied van de steenuil mogen alleen overdag worden uitgevoerd. Het directe leefgebied van de steenuil betreft het gebied in een straal van 250 meter om de broedlocatie van de steenuil heen.
15. De bomen met holen van spechten dienen voordat ze worden gekapt door een ter zake kundige1 gecontroleerd te worden op de aanwezigheid van de groene specht. Indien de holen in gebruik zijn, mogen de bomen nog niet worden gekapt en dient in overleg met de ter zake kundige1 een werkwijze te worden opgesteld waarmee de groene specht wordt ontmoedigd nog gebruik te maken van de holen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Bedrijventerrein Habraken" in de gemeente Veldhoven; ten noorden van de Heikantsebaan, ten oosten van de Oude Kerkstraat, ten westen van de Vooraard]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0281" userIdentity="Alterra1" derogation_reference="Alterra1-B-30-2009122416290014">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-02-22</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Aan de hand van de MER is het beste alternatief bepaald en dit is vervolgens opgenomen in het bestemmingsplan van de gemeente Deurne. Ten aanzien van meerdere locaties zijn verschillende criteria beschouwd, waaronder ‘biotoopverlies flora en fauna’, ‘beïnvloeding ecologische relaties’, ‘verstoring’ en ‘lichthinder natuurgebieden’. Aan het eerstgenoemde criterium is daarbij het meeste gewicht toegekend. U geeft aan dat de alternatievenafweging heeft plaatsgevonden op basis van een habitatgeschiktheidsanalyse van verschillende soortgroepen, die vergelijkbaar zou zijn met een quick-scan voor de Floraen faunawet. De huidige gekozen locatie (in de MER aangeduid als ‘locatie 2’) komt in de MER met betrekking tot de effectenbeschrijving ten opzichte van het criterium ‘biotoopverlies flora en fauna’ als meest gunstige naar voren. Er wordt vermeld dat de habitatgeschiktheid van deze locatie relatief laag is en dat er hier relatief weinig soorten zouden voorkomen. Dit wordt bevestigd door nader veldonderzoek ten aanzien van het gekozen alternatief. Het huidige plangebied wordt gekenmerkt door agrarisch gebruik (grote open ruimten) en betreft hoofdzakelijk veehouderijen. Ten aanzien van voornoemd ruimtegebruik en de uitgevoerde analyse, acht ik een dergelijke werkwijze voldoende om met betrekking tot de alternatievenafweging, tot een verantwoorde locatiekeuze te komen.
Ten aanzien van de verdere uitwerking van het gekozen alternatief is er onder meer voor gekozen het aanwezige lanenpatroon in het gebied, waaraan grote waarden worden toegekend, zoveel mogelijk in het plan te implementeren. Voorts bent u voornemens ten aanzien van de uitvoering van de werkzaamheden in het huidige plangebied zorgvuldig te handelen. Ik ben op grond van het bovengenoemde van mening dat het voorgenomen project ten aanzien van voorkomende (beschermde) soorten bevredigend tot een einde wordt gebracht. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">laanboom kappen</method>
		</methods>
		<reasons>
			<reason code="FT">De uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het verwijderen van de betreffende nestboom van de grote bonte specht dient plaats te vinden buiten de broedperiode van de soort. Aangezien er geen standaard broedperiode is, dient de betreffende boom voorafgaande aan het kappen daarvan door een ter zake kundige1 op de aanwezigheid van de grote bonte specht te worden gecontroleerd. Indien het nest in gebruik is, dient met kappen gewacht te worden tot de jongen zijn uitgevlogen.
8. De laanbomen in het plangebied, die zich bevinden langs bestaande, te handhaven infrastructuur, dienen zoveel mogelijk te worden behouden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[Projectvestiging glastuinbouw Deurne,]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0431" userIdentity="Alterra1" derogation_reference="Alterra1-B-31-2009122912361616">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-02-21</licenseValidFrom>
		<licenseValidUntil>2013-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Richtinggevend voor de ruimtelijke inrichting van het gebied zijn de streefbeelden en doelen vanuit vigerend beleid, zoals het streekplan, de beheersvisie Lendevallei 2003, de ontwikkelingsvisie Wolvega & de Zuidflank en het waterbeheerplan. Volgens het Integraal Waterbeheerplan dienen uiterlijk in 2016 alle kaden op hoogte te zijn en moet de bergingscapaciteit van de boezem vergroot worden. De activiteit is plaatsgebonden. Het doel van het project is om, naast natuurontwikkeling, de oude meanders van de Linde in ere te herstellen. Een andere locatie is dan ook niet aan de orde. De Linde maakt onderdeel uit van de Ecologische Hoofdstructuur (EHS), waarin herstel van beekdalsystemen, zoals de
Linde, centraal staat. Met de voorgestelde mitigerende maatregelen wordt aantasting van leefgebied van aanwezige soorten tot een minimum beperkt. De inrichting is gericht op verbetering van natuurwaarden en zal gunstig zijn voor de aanwezig beschermde soorten.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">omhakken nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Alle maatregelen dienen plaats te vinden onder toezicht van een ter zake kundige1]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Herinrichting Blesbroggepoolder en Swattediekien" in de gemeente Wolvega]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0470" userIdentity="Alterra1" derogation_reference="Alterra1-B-32-2009122913082086">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-02-22</licenseValidFrom>
		<licenseValidUntil>2010-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[De afwegingen die zijn gemaakt voor het inrichtingsplan zijn gedaan op basis van een groot aantal criteria. Zowel aspecten als veiligheid, hydrologie, natuur en landschap zijn hierin in meegenomen. Deze criteria zijn opgenomen in de MER-rapportage en geven een positief beeld voor de inrichting. De uitwerking van de inrichting in de toetsing aan de Flora en Faunawet geeft daarnaast aan dat de inrichting op vele beschermde soorten een positief effect zal hebben. De maatregelen zorgen dat het leefgebied aantrekkelijker wordt voor de vele beschermde diersoorten die in het gebied voorkomen. Door mitigerende maatregelen zal het tijdelijke verstoringeffect zo minimaal mogelijk worden ge-houden. Het is hiermee voldoende aangetoond dat voor het project geen gunstigere op-lossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">omhakken bomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[project "Rivierverruiming Lexkesveer"Wageningen]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0214" userIdentity="Alterra1" derogation_reference="Alterra1-B-33-2009122913182413">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-02-26</licenseValidFrom>
		<licenseValidUntil>2012-07-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[In het Streekplan Overijssel 2000+ is aangegeven dat door de ruimtelijke structuur van de dubbelkern Nijverdal/Hellendoorn er weinig mogelijkheden tot ontwikkeling van het dorp Hellendoorn bestaan. Woningbouw is echter noodzakelijk om de komende jaren te kunnen voorzien in de groeiende vraag naar woningen in de kern Hellendoorn. Aan de noord- en zuidzijde kan nog een geringe afronding plaatsvinden. Aan de noordzijde houdt deze verband met de gewenste aanleg van een randweg. Aan de zuidzijde is in de buurt van het Reestpark een geringe uitbreiding denkbaar, maar deze vormt geen alternatief voor de projectlocatie Hellendoorn-Noord. Alternatieve locaties waarbij negatieve effecten op de steenuil kunnen worden voorkomen zijn niet in die mate voorhanden, dat deze een goede alternatieve locatie vormen. De voorgestelde locatie sluit het meest aan bij de ontwikkeling van de gewenste randweg. Er worden voldoende compenserende maatregelen getroffen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">aantasten fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De aanleg van compenserend leefgebied dient conform bijlage 3 van het bij de aanvraag geleverde rapport “Projectplan aanvraag ontheffing Flora- en faunawet, Hellendoorn-Noord, Gemeente Hellendoorn”, d.d. 30 mei 2007 en de brief met aanvullende informatie van 17 januari 2008, uitgevoerd te worden. Deze compenserende maatregelen dienen geschikt te zijn voor de steenuil, vóórdat de verstorende werkzaamheden plaatsvinden.
8. De plaatsing van minimaal 4 nestkasten dient plaats te vinden vóórdat de verstorende werkzaamheden plaatsvinden. Deze nestkasten dienen, onder begeleiding van een ter zake kundige1 op het gebied van steenuilen, geplaatst te worden ten noorden van het plangebied.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Woningbouwontwikkeling Hellendoorn Noord" in de gemeente Hellendoorn, met Amersfoort coördinaten 226/490, 227/490 en 226/491.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="719316" userIdentity="Alterra1" derogation_reference="Alterra1-B-131-2010031517411766">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Flevoland]]></licensingAuthority>
		<licenseValidFrom>2008-08-26</licenseValidFrom>
		<licenseValidUntil>2008-10-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Garrulus glandarius]]></species>
		<regions>
			<region code="NL23">Flevoland</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[De activiteit moet vooraf gemeld worden (24 uur) via het emailadres faunamelding@flevoland.nl, voor vervolgacties langer dan een week moet een nieuwe melding worden gedaan. Binnen vier weken na afloop van de termijn waarvoor de ontheffing is verleend dient een verslag te worden uitgebracht over het gebruik van de ontheffing;]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[De houder van de ontheffing moet deze kunnen tonen aan toezichthouder op plaatsen waar de handelingen plaats vinden; 
De faunabeheerders in dienst van Stichting Faunabeheer Flevoland kunnen zich bij het gebruik van de ontheffing laten vergezellen door 4 jachtacte houders
Gebruik van de ontheffing is toegestaan nadat minimaal twee preventieve maatregelen uit het Handboek Faunaschade zijn genomen.]]></comments>
		<location><![CDATA[percelen gelegen aan de Sterappellaan 29 te Zeewolde]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="726473" userIdentity="Alterra1" derogation_reference="Alterra1-B-132-2010031518311660">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Flevoland]]></licensingAuthority>
		<licenseValidFrom>2008-09-16</licenseValidFrom>
		<licenseValidUntil>2008-04-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser anser, Anser albifrons]]></species>
		<regions>
			<region code="NL23">Flevoland</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[De activiteit moet vooraf gemeld worden (24 uur) via het emailadres faunamelding@flevoland.nl, voor vervolgacties langer dan een week moet een nieuwe melding worden gedaan. Binnen vier weken na afloop van de termijn waarvoor de ontheffing is verleend dient een verslag te worden uitgebracht over het gebruik van de ontheffing;]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[De houder van de ontheffing moet deze kunnen tonen aan toezichthouder op plaatsen waar de handelingen plaats vinden; 
De faunabeheerders in dienst van Stichting Faunabeheer Flevoland kunnen zich bij het gebruik van de ontheffing laten vergezellen door 4 jachtacte houders
Gebruik van de ontheffing is toegestaan nadat minimaal twee preventieve maatregelen uit het Handboek Faunaschade zijn genomen.
Afschot mag alleen plaats vinden op schade percelen.
Hooguit 2% van een groep kolganzen en/of grauwe ganzen mag worden afgeschoten. Indien er meer dan 500 ganzen in een groep zitten mogen er nooit meer dan 10 worden geschoten.
Afschot mag alleen plaats vinden als er geen vermenging is met kleine zwaan of wilde zwaan.
Afschot mag alleen plaats vinden van een half uur voor zonsopgang tot 12.00 uur 's middags.
Binnen gebieden die zijn aangewezen als foerageergebied voor overwinterende ganzen mag geen gebruik van de ontheffing worden gemaakt.]]></comments>
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		<comments></comments>
		<location><![CDATA[gehele provincie Friesland  voor zover gelegen buiten ganzenfoerageergebieden, NB-wetgebieden, VR-gebieden, HR-gebieden en natuurgebieden van TBO's]]></location>
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		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
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		<comments><![CDATA[Toegestane activiteit betreft slechts verontrusten! Niet toegestaan voor ganzen en smienten binnen ganzenfoerageergebieden tussen 1 oktober en 1 april. Overige soorten binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten (buiten foerageergebieden hele etmaal).]]></comments>
		<location><![CDATA[gehele provincie Friesland]]></location>
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		<comments><![CDATA[activiteit mag door jachthouders worden uitgevoerd in hun jachtveld (doden alléén met geweer).]]></comments>
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		<supervisoryMeasure><![CDATA[geen rapportage verplicht, dus aantallen niet bekend]]></supervisoryMeasure>
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		<comments><![CDATA[activiteit mag door jachthouders worden uitgevoerd in hun jachtveld (doden alléén met geweer).]]></comments>
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		<impactOnPopulation><![CDATA[onbekend]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[geen rapportage verplicht, dus aantallen niet bekend]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Activiteit mag door jachthouders worden uitgevoerd in hun jachtveld (doden alléén met geweer). Afstemming over periode van afschot tussen Nederlandse Postduivenhouders Organisatie, LTO en KNJV.]]></comments>
		<location><![CDATA[gehele provincie Friesland]]></location>
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		<sensitive>false</sensitive>
		<comments><![CDATA[Activiteit mag door Natuurmonumenten worden uitgevoerd op Griend en Schiermonnikoog. Tevens vangen en handmatig doden (alléén op Griend).]]></comments>
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		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
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		<sensitive>false</sensitive>
		<comments><![CDATA[Toegestane activiteit betreft slechts verontrusten met akoestische middelen en jachtvogels op de terreinen van Ecopark de Wierde te Oudehaske.]]></comments>
		<location><![CDATA[ Ecopark de Wierde te Oudehaske]]></location>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[All Aves]]></species>
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			<region code="NL12">Friesland (NL)</region>
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		<alternativesAssessed></alternativesAssessed>
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		<methods>
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		</reasons>
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			<otherNumber>0</otherNumber>
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			<individuals>10</individuals>
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			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Betreft bestrijding op het militair vliegveld Leeuwarden, tevens verontrusten van de betreffende diersoorten. Ook met jachtvogel en vanuit auto.]]></comments>
		<location></location>
		<licensedJustification><![CDATA[5 buizerds (Buteo buteo) en 5 torenvalken (Falco tinnunculus) gevangen en elders losgelaten.]]></licensedJustification>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser anser]]></species>
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		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>3064</individuals>
			<eggs>1311</eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/017/2005" userIdentity="Alterra1" derogation_reference="Alterra1-B-144-2010050611592301">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Larus ridibundus]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Afschot pas na toestemming provinciaal toezichthouder. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Tevens verontrusten.]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/018/2005" userIdentity="Alterra1" derogation_reference="Alterra1-B-145-2010050612020416">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Fulica atra]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>7</individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Afschot pas na toestemming provinciaal toezichthouder. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/021/2005" userIdentity="Alterra1" derogation_reference="Alterra1-B-146-2010050612050580">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Fulica atra]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>6</individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Afschot pas na toestemming provinciaal toezichthouder. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/022/2005" userIdentity="Alterra1" derogation_reference="Alterra1-B-147-2010050612065347">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Columba oenas]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Afschot pas na toestemming provinciaal toezichthouder. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Tevens verontrusten.]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/023/2005" userIdentity="Alterra1" derogation_reference="Alterra1-B-148-2010050612431569">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Sturnus vulgaris]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Afschot pas na toestemming provinciaal toezichthouder. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[nog geen rapportage ontvangen]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/024/2005" userIdentity="Alterra1" derogation_reference="Alterra1-B-149-2010050612484506">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Phasianus colchicus]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">onbekend</method>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Periode aansluitend op jachtperiode. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Alléén verontrusten.]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="Frl. 68/003/2008" userIdentity="Alterra1" derogation_reference="Alterra1-B-150-2010050612505155">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Friesland]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anas platyrhynchost]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">onbekend</method>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs></eggs>
			<nests></nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals></individuals>
			<breedingPairs></breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Periode aansluitend op jachtperiode. Binnen ganzenfoerageergebieden van 1 oktober tot 1 april van 12.00 uur tot zonsondergang, onder voorwaarde van in achtneming 500 meter afstand tot ganzen en smienten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[nog geen rapportage ontvangen]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2008-53895" userIdentity="Alterra1" derogation_reference="Alterra1-B-151-2010050613134935">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Groningen]]></licensingAuthority>
		<licenseValidFrom>2008-09-19</licenseValidFrom>
		<licenseValidUntil>2009-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Corvus frugilegus]]></species>
		<regions>
			<region code="NL11">Groningen</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>5</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[9. De gebruiker' van de ontheffing is verplicht binnen vier  weken na afloop van de termijn waarvoor de machtiging is verleend, een schriftelijk verslag uit te brengen aan de provincie Groningen, afdeling Landelijk Gebied en Water, team Groene Wetten, Postbus 630, 9700 AP, Groningen over de wijze waarop van de ontheffing gebruik is gemaakt, in die zin dat een opgave moet worden verstrekt van het aantal dieren dat in het kader van deze ontheffing is opgespoord, bemachtigd en gedood (alsmede de locaties, tijdstippen en data waarop dat is gebeurd). Wanneer geen gebruik is gemaakt van de ontheffing dient dit eveneens schriftelijk te worden gemeld bij de provincie Groningen.
11. Ringen die aan poten van gedode vogels worden aangetroffen moeten, onder vermelding van datum en plaats van afschot worden toegezonden aan het NIOO-CTE vogeltrekstation, Postbus 40, 6666 ZG, Heteren.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[8. Van deze ontheffing mag slechts gebruik worden gemaakt als er belangrijke schade is of dreigt te
ontstaan, en wanneer na gelijktijdig (aantoonbaar) inzetten van tenminste twee typen preventieve
verjaagmiddelen, te weten voldoende visuele afweermiddelen en voldoende akoestische afweermiddelen,
blijkt dat deze onvoldoende effect hebben. Voor een uiteenzetting van de beschikbare
preventieve middelen en de toepassing daarvan verwijzen wij naar het Handboek Faunaschade van
het Faunafonds.]]></comments>
		<location><![CDATA[Ter Apel]]></location>
		<licensedJustification><![CDATA[maximaal 5 per dag]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2008101" userIdentity="Alterra1" derogation_reference="Alterra1-B-152-2010050613284582">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2008-06-15</licenseValidFrom>
		<licenseValidUntil>2008-10-15</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Corvus frugilegus]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="21">Capture for decoy use</activity>
			<activity code="22">Capture (ringing)</activity>
			<activity code="81">Deliberate disturbance during the period of breeding</activity>
			<activity code="82">Deliberate disturbance during the period of rearing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
			<reason code="51">For the purposes of researching and education</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType><![CDATA[verplaatst]]></otherType>
			<otherNumber>394</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[spreeuwenpilot tbv schadereductie in de blauwe bessen teelt, ontheffing voor bessenteler. aantal verplaatste spreeuwen geldt voor 2008101 en 2008102]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2008102" userIdentity="Alterra1" derogation_reference="Alterra1-B-153-2010050613350265">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2008-06-15</licenseValidFrom>
		<licenseValidUntil>2008-10-15</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Corvus frugilegus]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="21">Capture for decoy use</activity>
			<activity code="22">Capture (ringing)</activity>
			<activity code="81">Deliberate disturbance during the period of breeding</activity>
			<activity code="82">Deliberate disturbance during the period of rearing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
			<reason code="51">For the purposes of researching and education</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[spreeuwenpilot tbv schadereductie in de blauwe bessen teelt, ontheffing voor bessenteler. aantal verplaatste spreeuwen geldt voor 2008101 en 2008102]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0424" userIdentity="Alterra1" derogation_reference="Alterra1-B-34-2009122913292575">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-02-25</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project is locatiespecifiek en volgt logisch op de voorgaande fasen. De huidige stand van zaken met betrekking tot beschermde diersoorten wordt geactualiseerd met nieuwe inventarisatiegegevens. Er is geen alternatief gevonden waarbij de aangetroffen soort
geen hinder ondervindt. Bij de uitvoering blijft er voldoende foerageergebied in de omgeving aanwezig en worden voldoende mitigerende maatregelen genomen. Het project, waarvoor ontheffing wordt aangevraagd, is probleemoplossend. Fase I en fase II moeten worden voltooid met fase III om het totale project tot een goed einde te brengen. Gezien de mitigerende en compenserende maatregelen, is het voorgestelde plan een bevredigend alternatief. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
Specifiek dient, bij het kappen van bomen met spechten en van de bomen binnen een straal van 50 meter daar omheen, rekening gehouden te worden met de broedperiode van de grote bonte specht en derhalve dient een ter zake kundige1 aanwezig te zijn die moet uitsluiten of er nog sprake van een broedgeval is.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[Project Stadsuitbreiding ‘Het Onderdijks’ te Kampen. Het plangebied is gelegen in de kilometerhokken X191-Y504, X191-505, X192-Y504 en X192-Y505]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0130A" userIdentity="Alterra1" derogation_reference="Alterra1-B-35-2009122913515988">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-03-04</licenseValidFrom>
		<licenseValidUntil>2008-09-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[84 different species]]></species>
		<regions>
			<region code="NL13">Drenthe</region>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="T002">Moving motor vehicles</method>
		</methods>
		<reasons>
			<reason code="12">In the interests of public safety</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. ’s Nachts dienen geen werkzaamheden plaats te vinden aan de damwanden en kades van het Meppelerdiep in verband met een rustmoment voor vogels.
8. Werkzaamheden dichtbij de belangrijke weidevogelgebieden dienen vanaf juli-eind september plaats te vinden.
9. De langs de oever aanwezige ruigte- en rietvegetatie dient voorafgaand gecontroleerd te worden op broedende vogels. Eventueel aanwezige vogels dienen verjaagd te worden.
10. De werkzaamheden dienen zoveel mogelijk vanaf het water van het Meppelerdiep plaats te vinden. De oeverzone dient zo smal als mogelijk te blijven.
11. Voorafgaand aan de werkzaamheden van 2008 dient de oever kort gemaaid te worden en kort te blijven gedurende de werkzaamheden. Het ongeschikt maken dient twee weken voorafgaand aan de werkzaamheden plaats te vinden.
12. De bovenstaande mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van broedvogels.
13. De bovenstaande mitigerende maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.
14. Natuurvriendelijke oevers en faunauittreedpassages dienen aangelegd te worden, conform de bij de aanvraag gevoegde kaart ‘Herstellen damwand en herstellen kades Meppelerdiep, concept bestek’ van Royal Haskoning, d.d. 19 februari 2006.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[de damwand en kades op de linkeroever (zuidoost) van het Meppelerdiep, tussen km 0,000 (Zwartsluis) en km 9,300 (vlak voor Meppel), in de gemeenten Zwartewaterland en Meppel]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0478" userIdentity="Alterra1" derogation_reference="Alterra1-B-36-2009122914124911">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-03-11</licenseValidFrom>
		<licenseValidUntil>2013-02-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis, Dendrocopos major, Accipiter nisus]]></species>
		<regions>
			<region code="NL34">Zeeland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het plangebied is één van de door het Rijk aangewezen prioritaire zwakke schakels van de Nederlandse kustverdediging. Door de verwachte zeespiegelstijging en de toenemende frequentie en intensiteit van de stormen, wordt het plangebied een veiligheidsknelpunt.
Dat wil zeggen dat het kustvlak niet voldoet aan de ‘1/4000 norm’. Dit betekent dat tussen nu en het jaar 2200 het kustvak niet bestand is tegen een storm, zoals die gemiddeld eens in de 4000 jaar plaatsvindt. Vervolgens zijn er alternatieven ontwikkeld om dit veiligheidsknelpunt op te lossen. Binnen deze alternatievenafweging is het aspect natuur meegenomen.
Uitgangspunt voor de kustversterking is naast het voldoen aan de veiligheidseisen, het verbeteren van de ruimtelijke kwaliteit en het versterken van de natuurwaarden. Om de reden hebben ‘zachte’ oplossingen (verbreden van de duinen) de voorkeur gekregen boven ‘harde’ oplossingen (aanleg van zeeweringen met asfalt of steenbekleding). Het plan voorziet in de verbreding van duinstrook en de aanleg van nieuw bos ter compensatie van het bos dat verloren gaat. De negatieve effecten op beschermde soorten zijn tijdelijk, terwijl de positieve effecten permanent zijn. De duinbiotoop breidt zich uit, wat positief is voor soorten die in de duinen broeden. Door de compensatie van het bos gaan de bosbewonende soorten er niet op achteruit. Gezien de zwakke zeewering ter plaatse zijn er geen alternatieve locaties voorhanden zijn. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht, grote bonte specht en de sperwer komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het verwijderen van de betreffende nestbomen van de groene specht, grote bonte specht en de sperwer dient plaats te vinden buiten de broedperiode van de betreffende soorten. De bomen in het werkgebied dienen maximaal twee weken voorafgaand aan de kapwerkzaamheden door een ter zake kundige1 te worden gecontroleerd op de aanwezigheid van broedgevallen van de groene specht, grote bonte specht en de sperwer.
8. Indien broedgevallen van voorgenoemde soorten worden aangetroffen, dienen de betreffende bomen te worden ontzien totdat is vastgesteld dat de betreffende soort de verblijfplaats niet meer als zodanig benut.
9. Het gekapte bos dient gecompenseerd te worden zoals aangegeven op figuur 3.3 van het bij de aanvraag geleverde rapport “Onderbouwing Ontheffingsaanvraag Zwakke Schakel Nolle Westduin, aanvulling op FF/75C/2007/0373” van 28 januari 2008 met rapport nummer 110502/ZF8/0F7/201571 en op de bij de aanvraag geleverde kaart “Zwakke schakels” met nummer ON060.30.001.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Zwakke schakels Nolle / Westduin Vlissingen" gemeente Vlissingen]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0473" userIdentity="Alterra1" derogation_reference="Alterra1-B-37-2009122914404307">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-03-20</licenseValidFrom>
		<licenseValidUntil>2013-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Dendrocopus major]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project heeft als doel 1600 woningen te realiseren op het voormalige bedrijventerrein van Enka, en maakt deel uit van het Masterplan Ede-Oost. In de Nota Ruimte is de regio Wageningen-Ede-Rhenen-Veenendaal aangewezen als economisch kerngebied. Het Masterplan Ede-Oost is hier de invulling van en is een raamwerk waarbinnen de verschillende deelgebieden, waaronder het Enka terrein, kunnen worden ontwikkeld. In het totale project
van Ede-Oost zullen tussen de 3500 en 4500 woningen worden gecreëerd om een kwaliteitsimpuls (wonen als werk) te geven aan de regio. Voor de locatie is mede gekeken naar verschillende kwaliteiten die het gebied Ede-Oost heeft, zoals de nabijheid van het station en de mogelijkheid van een directe ontsluiting op de A12. Het voormalige fabrieksterrein staat leeg en moet gesaneerd worden vanwege grote vervuiling. Voor alle soortgroepen vindt compensatie zodanig plaats dat de gunstige staat van de populaties niet in het geding komt. Door het realiseren van de voorgestelde maatregelen is zorgvuldig handelen gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd en de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[16. De bosopstanden dienen vóór de kap nogmaals te worden gecontroleerd op mogelijke verblijfplaatsen van de rosse vleermuis en de watervleermuis. Bij aantreffen van vleermuizen dient gewacht te worden totdat de soorten niet meer in de bomen aanwezig zijn.
17. De kapwerkzaamheden dienen plaats te vinden in de periode half maart tot half april of in de periode september-oktober.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[het project "Enkaterrein" aan de Dr. Hartogsweg ten oosten van Ede]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0557" userIdentity="Alterra1" derogation_reference="Alterra1-B-38-2009122914535857">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-01</licenseValidFrom>
		<licenseValidUntil>2009-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Strix aluco]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De betreffende wijk bestaat uit oudere bedrijfspanden van Philips. De bestaande bedrijfsbebouwing is niet bruikbaar meer, mede omdat hernieuwde bedrijfsvestiging hier niet acceptabel is vanwege de direct omsluitende woonbebouwing van Drents Dorp. In het plangebied is al bebouwing aanwezig en de nieuwbouw vindt plaats op dezelfde locatie. Omdat hier sprake is van efficiënt ruimtegebruik is er geen geschiktere locatie voorhanden
dan de huidig gekozen locatie. De boom met daarin een verblijfplaats van een bosuil dient uit veiligheidsoverwegingen gekapt te worden. Hiervoor is geen ander alternatief denkbaar dan tot kap over te gaan. Met betrekking tot inrichtingsalternatieven heeft u ervoor gekozen om de nieuwe woningen deels aan te passen aan de eisen die vleermuizen stellen aan hun omgeving. Ook met betrekking tot de wijze van uitvoering van de sloop en de kap houdt u voldoende rekening met de aanwezigheid van vleermuizen en de bosuil. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voor het project voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestboom kappen</method>
		</methods>
		<reasons>
			<reason code="FT">oonder andere aangewezen de uitvoering
van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de bosuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
De boomgroep in de zuidoosthoek van het plangebied dient, direct voorafgaand aan de kapwerkzaamheden, geïnventariseerd te worden op de aanwezigheid van de bosuil. Indien de holte in gebruik is, dient met een ter zake kundige1 te worden overlegd welke werkwijze gehanteerd dient te worden om de bosuil er toe te bewegen zelfstandig de holte te verlaten.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Strijp fase 1’"in de gemeente Eindhoven.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0025" userIdentity="Alterra1" derogation_reference="Alterra1-B-39-2009122915162309">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-03-27</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[IHet project vormt een onderdeel van een woningbouwplan, dat al grotendeels is afgerond.
De locatie is reeds lange tijd in beeld voor woningbouw. Al in de structuurvisie Twello 1981 is de locatie concreet opgenomen geweest voor woningbouw. De werkzaamheden zijn locatiegebonden; een onderzoek naar alternatieve locaties is daarom niet aan de orde. Er worden voldoende maatregelen getroffen waardoor de gunstige staat van instandhouding van de steenuil niet in het geding komt. Hiermee is het voldoende aangetoond dat voor een bevredigende oplossing voor het project gekozen is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">aantasten fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De mitigerende en compenserende maatregelen dienen uitgevoerd te worden conform de brief van 7 maart 2008 met aanvullende informatie, getiteld ‘Uiteenzetting ontheffingsaanvraag compensatieplan. Behorend bij de ontheffingsaanvraag Flora en faunawet nummer FF/75C/2008/0025. Ten behoeve van de ontwikkeling van 14 woningen aan de Veenhuisweg/H.W. Iordensweg te Twello’.
8. De mitigerende en compenserende maatregelen dienen begeleid te worden door een ter zake kundige1 op het gebied van steenuilen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project ‘Woningbouw Veenhuisweg Twello’ in de gemeente Voorst aan de de H.W. Iordensweg, Veenhuisweg en De Hoeven]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0406" userIdentity="Alterra1" derogation_reference="Alterra1-B-40-2009122915423504">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-05-01</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[IHet project betreft de bouw van een woonwijk met een oppervlakte van circa 86 hectare.
Binnen de stedelijke regio Uden-Veghel heeft de gemeente Uden een prominente functie toebedeeld gekregen voor de opvang van de regionale woningbehoefte. Er heeft een locatie afweging plaatsgevonden. Ten tijden van het opstelen van het uitwerkingsplan was de aanleg van de A50 aan de westzijde van Uden reeds in gang gezet. De aanleg van deze weg betekent een afgrenzing van Uden aan de westzijde. Het ontwikkelen van grootschalige woningbouw aan de westzijde van de A50 zal integratie van de nieuwe wijk met de bestaande stad in de weg staan. Aan de oostzijde van de gemeente ligt de nadruk op de opvang van economische functies. Hierdoor zijn er onvoldoende mogelijkheden om een aantrekkelijk woonmilieu te realiseren. Het gebied ten noorden van Uden wordt begrensd door een kwetsbaar natuurgebied de Maashorst. Grootschalige woningbouw zou een aantasting betekenen van de kwaliteiten in dit gebied. Om deze redenen is er gekozen voor de huidige planlocatie. Het project, waarvoor ontheffing wordt aangevraagd, is probleemoplossend, omdat de natuurwaarden op de huidige planlocatie grotendeels behouden kunnen worden en/of worden gemitigeerd en deels gecompenseerd. Woningbouw op deze locatie heeft de minste negatieve gevolgen voor de natuurwaarden rondom Uden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voor het project voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouw met nestlocatie</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De sloopwerkzaamheden dienen uitgevoerd te worden in de voor de steenuil minst kwetsbare
periode, zijnde de periode van half september tot eind januari.
8. De sloopwerkzaamheden dienen uiterlijk om 6.00 uur ’s morgens te starten. Dit om te voorkomen dat de steenuil voor aanvang van elke sloopdag terugkeert.
9. Voorafgaand aan de start van de sloopwerkzaamheden dient het te slopen gebouw elke ochtend door een ter zake kundige1 op het gebied van uilen gecontroleerd te worden op de aanwezigheid van de steenuil, totdat de ter zake kundige1 van mening is dat het gebouw dusdanig ongeschikt is dat de steenuil geen gebruik meer zal maken van het gebouw. Bij aanwezigheid dient te worden gewacht met de werkzaamheden totdat de steenuil het gebouw verlaten heeft.
10. Om de broedgelegenheid van de steenuil te waarborgen, dienen voorafgaand aan de sloop van de boerderij twee nestkasten opgehangen te worden net even buiten het plangebied, op maximaal 500 meter van de huidige locatie. Bij het ophangen van nestkasten voor de steenuil dienen de volgende voorwaarden gevolgd te worden:
·  De nestkasten dienen zodanig te worden geplaatst dat deze nimmer in het volle zonlicht komen te staan. Bij de plaatsing van een nestkast aan en/of in een gebouw dient een schaduwrijke, noordelijk gerichte gevel te worden gekozen;
·  De nestkasten dienen op rustige locaties te hangen, met voldoende dekking;
·  De nestkasten dienen 2 tot 4 meter boven het maaiveld te worden geplaatst;
·  De nestkasten dienen zodanig te worden geplaatst dat de uilen bij het af- en aanvliegen geen weg hoeven te passeren, om verkeersslachtoffers te voorkomen. Ook dienen de kasten niet boven water gehangen te worden, om mogelijke verdrinking van nog niet vliegvlugge jongen te voorkomen.
·  Voor de exacte locatie dient een ter zake kundige1 op gebied van uilen te worden geraadpleegd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Woonwijk Velmolen te Uden" , Lippstadtsingel, Vloetrand en woonwijk Mintmeester]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0456" userIdentity="Alterra1" derogation_reference="Alterra1-B-41-2009122915571610">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-10</licenseValidFrom>
		<licenseValidUntil>2009-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[0]]></numberOfLicenses>
		<species><![CDATA[Corvus frugilegus]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project betreft de ontwikkeling van een woonwijk ter plaatse van het vroegere ziekenhuiscomplex MCL Noord in Leeuwarden. Op het terrein bevinden zich talrijke monumentale en waardevolle bomen. De kwaliteit van de te realiseren woonwijk wordt onder meer gevormd door het aanwezige groen. Bij het tot stand komen van het stedenbouwkundige plan zijn diverse inrichtingsvarianten beoordeeld, waarbij de aanwezige bomen maximaal zijn ingepast in het plan. Alleen de bomen die niet gehandhaafd kunnen worden ten gevolge van de aanleg van infrastructuur en woningen zullen gekapt worden.
Daarnaast worden enkele bomen verwijderd waarvan de vitaliteit gering is. De gekozen werkwijze zorgt ervoor dat de negatieve effecten tot een minimum beperkt. Schade aan de gunstige staat van instandhouding van de roek is dan ook niet te verwachten. Hiermee is het voldoende aangetoond dat voor een bevredigende oplossing voor het project gekozen is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestboom kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de roek komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[project Ontwikkeling Bonifatiuspark, Leeuwarden’; Mr. P.J. Troelstraweg, Dammelaan, Jelsumerstraat en Valkstraat]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art 65 prov vrijstellingen" userIdentity="Alterra1" derogation_reference="Alterra1-B-154-2010050615021122">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2008-01-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser fabalis, Anser albifrons, Anser anser, Anas platyrhynchos, Columba oenas, Sturnus vulgaris, Passer montanus, Passer domesticus, Fulica atra, Cygnus olor, Corvus frugilegus, Pica pica, Phasianus colchicus]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="81">Deliberate disturbance during the period of breeding</activity>
			<activity code="82">Deliberate disturbance during the period of rearing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2005104-10, 2005105-12, 2005106-9" userIdentity="Alterra1" derogation_reference="Alterra1-B-155-2010050615090002">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2005-07-05</licenseValidFrom>
		<licenseValidUntil>2010-07-05</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser anser]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>945</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[gering want gelimiteerd op max 2 vogels per invallende groep]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[losse ontheffingen voor Noord-, Midden- en Zuid-Limburg uit de tijd dat er nog 3 FBE's waren,  genoemd aantal geldt voor de winter 07-08]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2005104-10, 2005105-12, 2005106-9" userIdentity="Alterra1" derogation_reference="Alterra1-B-156-2010050615135815">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2005-07-05</licenseValidFrom>
		<licenseValidUntil>2010-07-05</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser albifrons]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>336</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[gering want gelimiteerd op max 2 vogels per invallende groep]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[losse ontheffingen voor Noord-, Midden- en Zuid-Limburg uit de tijd dat er nog 3 FBE's waren,  genoemd aantal geldt voor de winter 07-08]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2007107-1; 2007106-1,2,3; 2007108-1" userIdentity="Alterra1" derogation_reference="Alterra1-B-157-2010050615150728">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2007-07-03</licenseValidFrom>
		<licenseValidUntil>2009-09-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser anser]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>405</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[gering want gelimiteerd op max 2 vogels per invallende groep]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[losse ontheffingen voor Noord-, Midden- en Zuid-Limburg uit de tijd dat er nog 3 FBE's waren, overzomerende grauwe gans]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2005104-11; 2005105-13; 2005106-10" userIdentity="Alterra1" derogation_reference="Alterra1-B-158-2010050615294020">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2005-07-05</licenseValidFrom>
		<licenseValidUntil>2010-07-05</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Corvus frugilegus]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>150</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[gering want max 250 voor geheel Limburg]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[losse ontheffingen voor Noord-, Midden- en Zuid-Limburg uit de tijd dat er nog 3 FBE's waren]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2005104-12; 2005105-14; 2005106-11" userIdentity="Alterra1" derogation_reference="Alterra1-B-159-2010050615323811">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Limburg]]></licensingAuthority>
		<licenseValidFrom>2005-07-05</licenseValidFrom>
		<licenseValidUntil>2010-07-05</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Sturnus vulgaris]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>1383</individuals>
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			<otherType></otherType>
			<otherNumber></otherNumber>
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		<populationSize>
			<individuals>0</individuals>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[aanwezig]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Jaarlijks moet het gebruik van de ontheffing worden gerapporteerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[losse ontheffingen voor Noord-, Midden- en Zuid-Limburg uit de tijd dat er nog 3 FBE's waren]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 68 - ontheffingen voor specifieke gevallen" userIdentity="Alterra1" derogation_reference="Alterra1-B-160-2010050618030758">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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		<species><![CDATA[Anas platyrhynchos]]></species>
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			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
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			<otherType></otherType>
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		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[2 WBE gebieden]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 68 - ontheffingen voor specifieke gevallen" userIdentity="Alterra1" derogation_reference="Alterra1-B-161-2010050618073894">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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		<species><![CDATA[Anas platyrhynchos]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
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		<reasons>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
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		<actuallyTaken>
			<individuals></individuals>
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		</actuallyTaken>
		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[10 WBE gebieden]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 68 - ontheffingen voor specifieke gevallen" userIdentity="Alterra1" derogation_reference="Alterra1-B-162-2010050618590436">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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		<species><![CDATA[Anser anser]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
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		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 WBE gebied]]></comments>
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	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 68 - ontheffingen voor specifieke gevallen" userIdentity="Alterra1" derogation_reference="Alterra1-B-163-2010050619001314">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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		<species><![CDATA[Anser anser]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
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		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
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		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
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		<comments><![CDATA[1 agrarisch gebied]]></comments>
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		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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			<region code="NL21">Overijssel</region>
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		<alternativesAssessed></alternativesAssessed>
		<activities>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
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		<actuallyTaken>
			<individuals></individuals>
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		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
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		<comments><![CDATA[1 WBE gebied]]></comments>
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		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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			<region code="NL21">Overijssel</region>
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		<alternativesAssessed></alternativesAssessed>
		<activities>
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		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
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			<individuals></individuals>
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		<actuallyTaken>
			<individuals></individuals>
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			<otherType></otherType>
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		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 WBE gebied]]></comments>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 68 - ontheffingen voor specifieke gevallen" userIdentity="Alterra1" derogation_reference="Alterra1-B-166-2010050619055702">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
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		<species><![CDATA[Anas platyrhynchos]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
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		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
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		<reasons>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
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			<otherType></otherType>
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		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding aan FBE]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[heel Overijssel]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 68 - ontheffingen voor specifieke gevallen" userIdentity="Alterra1" derogation_reference="Alterra1-B-167-2010050619073130">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
		<licenseValidFrom>2008-10-20</licenseValidFrom>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Passer domesticus]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
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		<reasons>
			<reason code="11">In the interests of public health</reason>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
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			<otherType></otherType>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
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			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[melding regiopolitie]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[voedingsmiddelenproducent]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 65 - vrijstellingen van schadesoorten" userIdentity="Alterra1" derogation_reference="Alterra1-B-168-2010050619114611">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
		<licenseValidFrom>2008-10-08</licenseValidFrom>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Corvus frugilegus]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
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		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
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			<otherType></otherType>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
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			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[alleen door grondgebruiker]]></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="art. 65 - vrijstellingen van schadesoorten" userIdentity="Alterra1" derogation_reference="Alterra1-B-169-2010050619175522">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Overijssel]]></licensingAuthority>
		<licenseValidFrom>2008-10-08</licenseValidFrom>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Branta leucopsis,  Pica pica, Phasianus colchicus, Anser anser, Columba oenas]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
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		<methods>
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		<reasons>
			<reason code="31">To prevent serious damage to crops</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals></individuals>
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			<otherType></otherType>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
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			<otherType></otherType>
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		</actuallyTaken>
		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[geen]]></impactOnPopulation>
		<supervisoryMeasure></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2008INT220835" userIdentity="Alterra1" derogation_reference="Alterra1-B-170-2010050619342988">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Utrecht]]></licensingAuthority>
		<licenseValidFrom>2008-04-15</licenseValidFrom>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser anser]]></species>
		<regions>
			<region code="NL31">Utrecht</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
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		<methods>
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		<reasons>
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		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
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			<individuals></individuals>
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			<otherType></otherType>
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		</licensed>
		<actuallyTaken>
			<individuals></individuals>
			<eggs>0</eggs>
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			<otherType></otherType>
			<otherNumber></otherNumber>
		</actuallyTaken>
		<populationSize>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[-]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[-]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[-]]></comments>
		<location><![CDATA[oostelijke binnenpolders van Tienhoven]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="2008INT221789" userIdentity="Alterra1" derogation_reference="Alterra1-B-171-2010050619524720">
		<licensingAuthority><![CDATA[Gedeputeerde staten van de provincie Utrecht]]></licensingAuthority>
		<licenseValidFrom>2008-05-01</licenseValidFrom>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Anser anser, Anser albifrons, Branta leucopsis]]></species>
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		<methods>
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		<impactOnPopulation><![CDATA[-]]></impactOnPopulation>
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		<comments><![CDATA[lokmiddelen niet toegestaan]]></comments>
		<location><![CDATA[diverse locaties gelegen in het werkgebied van de FBE Utrecht]]></location>
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		<comments><![CDATA[overzomerend]]></comments>
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	</derogation>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-09</licenseValidFrom>
		<licenseValidUntil>2011-09-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Naar aanleiding van binnengekomen reacties van omwonenden is besloten om het getoetste ‘definitieve’ stedenbouwkundig ontwerp op onderdelen aan te passen. De rij aan de noordzijde van deelgebied Oost (achterzijde woningen van de straat Logterheuvel) zal niet worden verkaveld. Om het aantal woningen in het plan gelijk te houden, worden deze elders in deelgebied oost ingepland. Het definitieve stedenbouwkundig ontwerp is derhalve op dit onderdeel nogmaals aangepast. De geplande kavels in de bosstrook zijn naar het zuiden verplaatst. De te bebouwen oppervlakte en de hoeveelheid te kappen bos zijn hierbij gelijk gebleven ten opzichte van het oorspronkelijke ‘definitieve’ ontwerp. In deze nieuwste verkaveling is zoveel mogelijk rekening gehouden met de natuurwaarden in het bos. Door buiten het broedseizoen van de grote bonte specht te werken wordt er voldoende zorgvuldig gehandeld. Er blijven tevens voldoende alternatieve broedplaatsen voor de soort aanwezig waardoor de gunstige staat van instandhouding niet in het geding komt. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
11. De bomen met holten van de grote bonte specht dienen gekapt te worden buiten het broedseizoen van deze soort.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments></comments>
		<location><![CDATA[Project "Dichterbijterrein (Vizier) te Gennep"; Stiemensweg en Heijenseweg]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0089" userIdentity="Alterra1" derogation_reference="Alterra1-B-43-2009122916223258">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-10</licenseValidFrom>
		<licenseValidUntil>2009-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL12">Friesland (NL)</region>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project betreft de sloop van een boerderij en de bijbehorende opstallen. De boerderij verkeert in vergaande vorm van verval. De bouwtechnische constructie van de oude boerderij is erg slecht. De voorgevel dreigt het elke moment te begeven. Hoewel het desbetreffende terrein is afgezet kan de veiligheid ter plaatse niet meer worden gegarandeerd. Naast de boerderij staan een ligboxenstal en een jongveestal. Deze bedrijfsgebouwen zijn afgedekt met sterk verouderde en broze asbestplaten.
Door de harde wind zijn er verschillende asbestplaten van de daken afgewaaid. Die platen komen uiteindelijk in het omringende gebied (weiland) terecht. Deze situatie kan alleen maar verslechteren (er zitten nu gaten in de daken) bij toenemende wind. Hiermee komt ook de volksgezondheid in het geding. Om redenen van veiligheid en volksgezondheid en vanwege brandrisico dient de bebouwing gesloopt te worden. Er zijn dan ook geen alternatieven voor het project aanwezig. Vanuit ecologisch standpunt is het ook geen optie om niks te doen, aangezien de huidige verblijfplaats van de kerkuil dan ook zal verdwijnen.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voor het project voorhanden is.
Hoewel de bestemmingsplannen en de MER’s relatief globaal zijn opgesteld en niet tot op soortniveau doordringen, zijn naar mijn mening in de opgestelde plannen wel de meest waardevolle gebieden ontzien door de gemaakte keuzes in alternatieven. Hierdoor worden met betrekking tot vele beschermde soorten geen verbodsbepalingen overtreden en wordt schade zoveel mogelijk voorkomen. Een eerder voorgesteld alternatief voor de compensatie voor de kerkuil en de steenuil was geen optie, omdat het gelegen is in een gebied waar, in de nabije toekomst, een nieuwe bestemming wordt opgelegd ten nadele van het voortbestaan van de compensatie. Het project, waarvoor ontheffing wordt aangevraagd, is wel probleemoplossend. De nu geplande compensatie voor kerkuil en steenuil kan voor een langere periode duurzaam behouden worden.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouw</method>
		</methods>
		<reasons>
			<reason code="11">In the interests of public health</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Voor aanvang van de sloop van de boerderij dient een ter zake kundige1 op het gebied van uilen te controleren of er kerkuilen aanwezig zijn en/of broeden in het gebouw. Indien de kerkuilen nog niet aan het broeden zijn, kan er overgegaan worden tot sloop op een tijdstip dat de kerkuilen niet aanwezig zijn in het gebouw. Als er echter sprake is van een broedgeval, dient er gewacht te worden met de sloop tot na het broedseizoen van de kerkuil.
8. De compenserende maatregelen dienen uitgevoerd te worden zoals beschreven in paragrafen 6 en 7 van de bij de ontheffingsaanvraag meegestuurde ‘Projectomschrijving sloop boerderij onder Folsgare (bijlage)’.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project ‘Sloop boerderij te Folsgare" in de gemeente Wymbritseradiel; Folsgeasterleane in Folsgare]]></location>
		<licensedJustification><![CDATA[Door de voorgenomen maatregelen zullen de volgende uilennesten verdwijnen:
·  Eén in 2005 voor het laatst gebruikte nestkast van een kerkuil en een in gebruik zijnde roestplaats van een steenuil in de grote schuur bij Heierhoeve;
·  Eén in 2006 gebruikte nestkast van een kerkuil in een paardenstal;
·  In de schuur op locatie (205,1x379,9) ten westen van de Annahoeve]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0350A" userIdentity="Alterra1" derogation_reference="Alterra1-B-44-2009122918033878">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-05-26</licenseValidFrom>
		<licenseValidUntil>2013-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[IHet alternatievenonderzoek heeft geleid tot de keuze om het tracé zoveel mogelijk lijnvormige elementen in het landschap te laten volgen, zodat doorsnijding van de aanwezige elementen beperkt blijft. In de uitwerking komt dit naar voren doordat is aangesloten op de waterlopen Heterensche Leigraaf en Eldensche Zeeg. Bij het verschuiven van het traject naar het noorden zal het tracé door meerdere steenuilenhabitats gaan. Bij het verschuiven van het tracé naar het zuiden komen de homeranges van de steenuilen van Homoet dichterbij. Een tracé ten zuiden van het geplande tracé lijkt iets gunstiger voor de steenuil dan een noordelijk tracé. Het meest zuidelijke tracé doorsnijdt dan wel een tweetal bosjes (Liendermeint en Bremerton). De schade hiervan is aanzienlijk groter voor de natuurwaarden. Bij de inpassing van het tracé in het bestaande water- en wegennetwerk is ook gekozen voor een goede oplossing. Ook worden voldoende mitigerende en compenserende maatregelen getroffen, zodat de gunstige staat van instandhouding van de beschermde soorten niet in het geding komt. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">schaden van nestlocatie</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Tussen kilometerpunt 2,1 en 5,4 van het tracé dient een haag aangelegd te worden. Deze haag dient minimaal 1 meter hoog te zijn. Deze haag dient binnen 5 meter aan beide kanten van de nieuwe weg te worden geplaatst.
9. In de omgeving van Homoet dienen minimaal 10 nestkasten geplaatst te worden.
10. In de omgeving van Homoet dient 1 hoogstamboomgaard met 10 bomen of 2 hoogstamboomgaarden met 5 bomen (met palen en bescherming) aangelegd te worden.
11. De bovenstaande voorwaarden 7 tot en met 10 dienen onder begeleiding van een ter zake kundige1 op het gebied van steenuilen plaats te vinden.
12. De plaatsing van nestkasten en fruitbomen dient gerealiseerd te zijn vóór december 2008 - januari 2009.
13. De locaties waar de nestkasten en boomgaarden geplaatst worden dienen vooraf ter informatie aan Dienst Regelingen gestuurd te worden]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "N837 Arnhem-Heteren" ten oosten van Herenen tussen de dorpen Driel en Elst]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0071" userIdentity="Alterra1" derogation_reference="Alterra1-B-45-2009123115060206">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-25</licenseValidFrom>
		<licenseValidUntil>2010-02-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[U acht het noodzakelijk om schaalvergroting op de bedrijfsvoering toe te passen. De ontwikkelingen in de huidige glastuinbouw zijn volgens u hier de oorzaak van. De noodzaak wordt verder vergroot door de stijgende kostprijzen van het product ten opzichte van de opbrengstprijzen. Uitbreiding is mogelijk binnen de vigerende beleidskaders. In zowel het Streekplan, het Gebiedsplan Wijde Biesbosch en in de Beleidsnota Glastuinbouw wordt het gebied Hongerenburg aangeduid als doorgroeigebied voor glastuinbouw. Een alternatief voor de ontwikkeling is praktisch onmogelijk. Het saneren van de huidige locatie en elders volledig nieuw bouwen is niet mogelijk, omdat de locatie praktisch onverkoopbaar zou zijn. Het project, waarvoor ontheffing wordt aangevraagd, is probleemoplossend. U heeft ingespeeld op compensatie ten opzichte van de huidige situatie door het behoud van een deel van de bestaande groenelementen en verbetering van de kwaliteit van vliegroutes en foerageergebieden van vleermuizen, maar ook steenuilen.
Op deze wijze draagt u zelfs bij aan een verbetering ten opzichte van de huidige situatie, omdat er verbindingen tussen bestaande vliegroutes worden hersteld. U neemt verder voldoende voorzorgsmaatregelen om negatieve effecten van lichtuitstoot tegen te gaan en te werken in de minst kwetsbare periode. Met bovenstaande gegevens heeft u voldoende alternatieven aangedragen met betrekking tot de inrichting van het plangebied en de te hanteren werkwijze. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">aantasting fourageergebied en</method>
		</methods>
		<reasons>
			<reason code="33">To prevent serious damage to forests</reason>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Alle mitigerende en compenserende maatregelen die zijn verwoord in de bij de aanvraag gevoegde projectomschrijving “Glastuinbouwontwikkeling in het doorgroeigebied Hongerenburg, Haarsteeg (gemeente Heusden)” dienen te worden uitgevoerd vóór de aanvang van de werkzaamheden.
9. De beplantingsvrije zones om de bestaande en toekomstige kascomplexen dienen te worden ingericht met ruige overhoeken; deze doen dienst als foerageergelegenheid voor de steenuil. Dit dient te gebeuren onder begeleiding van een ter zake kundige1.
10. Om zoveel mogelijk verstoring te voorkomen, dienen de werkzaamheden zich te beperken tot de ruimte die daadwerkelijk noodzakelijk is om het project uit te kunnen voeren.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Ontwikkeling glastuinbouw bij Kwekerij De Hungerenburcht"; Tuinbouwweg 94, te haarsteeg]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0010" userIdentity="Alterra1" derogation_reference="Alterra1-B-46-2009123115224504">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-04-28</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Picus viridis]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De keuze van de locatie Volgerlanden-Oost is vooral bepaald door het maatschappelijk belang en de beperkte keuzemogelijkheden voor grote woonwijken in de regio Drechtsteden. Alternatieven voor dergelijke grote woonwijken in deze regio stuiten op dezelfde vergelijkbare ecologische bezwaren als welke zich op de actuele locatie voordoen.
De Volgerlanden-Oost maakt deel uit van de VINEX-wijk ‘De Volgerlanden’ en de alternatievenafweging is vooral bepaald door het overheidsbeleid. Hierdoor zal ook op een alternatieve locatie verstoring van beschermde soorten optreden. Door het nemen van mitigerende maatregelen wordt verstoring van de beschermde soorten zoveel mogelijk voorkomen. De soorten waarvoor ontheffing wordt aangevraagd zijn verder niet zeer zeldzaam en kunnen naar verwachting elders leefgebied vinden, waardoor de gunstige staat van instandhouding van deze soorten door dit project niet in het geding is. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen, aantasting fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd en groene specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
6. De compenserende en mitigerende maatregelen genoemd in de bij de aanvraag gevoegde ”Projectomschrijving ‘De Volgerlanden-Oost’ van december 2007, dienen te worden uitgevoerd met in achtneming van onderstaande voorwaarden.
7. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de soort(en) waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (voortplanting, winterrust) te voorkomen.
8. Vóór de aanvang van kapwerkzaamheden dienen de boom met het buizerdnest en potentiële nestbomen van de groene specht te worden gecontroleerd door een ter zake kundige1 op het gebied van vogels, op de aanwezigheid van vogels op het nest of in de holtes buiten het broedseizoen.
9. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project ‘De Volgerlanden - Oost’ in de gemeente Hendrik-Ido-Ambacht; Vrouwgelenweg, de Onderdijkserijweg en de bebouwde kom van Hendrik-Ido-Ambacht]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0516" userIdentity="Alterra1" derogation_reference="Alterra1-B-47-2009123115293968">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-05-13</licenseValidFrom>
		<licenseValidUntil>2010-03-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Dendrocopos major, Athene noctua]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De keuze voor de locatie van het project is vooral tot stand gekomen omdat het gebied aan de Oude Twentseweg is aangewezen als landbouwontwikkelingsgebied. Binnen een landschapsontwikkeling past een schaalvergroting zoals deze. De definitieve plaatsing van het bouwblok is nog niet vastgesteld. Gezien de beschikbare ruimte is de plaatsing, zoals is aangegeven in het inrichtingschets het meest logisch, landschappelijk verantwoord en het meest efficiënt. Verschuiving van het bouwblok naar het zuiden zodat bos bespaard kan blijven is geen optie, aangezien hier een hoofdgasleiding ligt. Verschuiving van het bouwblok naar het westen is geen optie, omdat deze gronden niet in uw eigendom zijn. Het bos wordt zoveel mogelijk gespaard en het gedeelte wat verdwijnt wordt gecompenseerd.
De aanwezige soorten zullen daarom ook na de inrichting gebruik blijven maken van het terrein. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen, aantasting fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>4</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd, grote bonte specht en de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Vóór de kap van de bomen dienen aanwezige holten door een ter zake kundige1 gecontroleerd te worden op het voorkomen van de grote bonte specht.
8. Oude bomen op de scheiding van het te kappen bos en het resterende bosgedeelte, dienen zo min mogelijk gekapt te worden.
9. In het resterende bos dient verstoring ten tijde van de werkzaamheden geminimaliseerd te worden ten behoeve van de grote bonte specht.
10. Voor de steenuil dienen onder begeleiding van een ter zake kundige1 op het gebied van steenuilen vóór het begin van de werkzaamheden drie steenuilen kasten opgehangen te worden in de directe omgeving.
11. Een ter zake kundige1 op het gebied van steenuilen dient vóór het begin van de sloopwerkzaamheden de loopstal te laten inspecteren op het voorkomen van de steenuil. Indien aangetroffen dient er gewacht te worden met de sloop werkzaamheden tot na de broedperiode.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA["Projectplan landbouwontwikkeling Oude Twentseweg 10, Hellendoorn”. Het plangebied ligt ten noordoosten van Hellendoorn aan de Oude Twentseweg 10]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0417" userIdentity="Alterra1" derogation_reference="Alterra1-B-48-2009123115394241">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-07-01</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De huidige processen (verdroging, successie) in de Zouweboezem leiden (op termijn) tot een sterke achteruitgang van kwantiteit en kwaliteit van het leefgebied van kwalificerende soorten van het Habitatrichtlijn- en Vogelrichtlijn-gebied ‘Zouweboezem’. Herstelmaatregelen zijn noodzakelijk om deze processen te keren en voldoende kwantiteit en kwaliteit van leefgebied te waarborgen zodat de instandhoudingsdoelen gehaald kunnen (blijven) worden. De werkzaamheden zijn bedoeld om de habitats van verschillende (beschermde) soorten ter plekke kwalitatief en kwantitatief te verbeteren. De werkzaamheden kunnen dan ook niet op een andere locatie worden uitgevoerd. Er is gekozen om met een cutterzuiger te werken om met het baggeren het beoogde resultaat te kunnen bereiken; zo wordt het reliëf onder water in stand gehouden.
De gekozen periode om de werkzaamheden uit te voeren is voor de meeste beschermde soorten gunstig. Het project, waarvoor ontheffing wordt aangevraagd, is probleemoplossend. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing
voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="41">For the protection of wild flora</reason>
			<reason code="42">For the protection of wild fauna</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
9. Vóór de aanvang van kapwerkzaamheden in een bos en/of andere houtopstand, dienen de te kappen bomen door een ter zake kundige1 op het gebied van vogels te worden gecontroleerd op de aanwezigheid van de grote bonte specht in holtes buiten het broedseizoen. Indien zich alleen vliegvlugge vogels in de nestboom bevinden, dienen deze voorafgaand aan de werkzaamheden te worden verjaagd.
16. De bovengenoemde mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de beschermde diersoorten waarvoor ontheffing wordt verleend.
17. De bovenstaande mitigerende maatregelen dienen in een ecologisch werkprotocol opgenomen te worden. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol uitgevoerd te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Herstelmaatregelen Zouweboezem" in de gemeente Zederik, gelegen tussen Sluis en Meerkerk]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0001" userIdentity="Alterra1" derogation_reference="Alterra1-B-49-2009123115511081">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-05-19</licenseValidFrom>
		<licenseValidUntil>2013-09-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL11">Groningen</region>
		</regions>
		<alternativesAssessed><![CDATA[De sloop van de schuur is een onderdeel van de uitvoering van het project Meerstad Deelplan 1, waarvoor eerder ontheffing is verleend met kenmerk FF/75C/2007/0021. De nut en noodzaak van het project zijn in dat besluit beoordeeld. Er zijn geen alternatieven onderzocht. In verband met toekomstige herinrichtingsplannen, dienen de schuren van de boerderij aan de Hoofdweg 179 te Harkstede gesloopt te worden. Het voorstel om het Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Er wordt geen afbreuk gedaan aan een gunstige staat van instandhouding van de soort]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De voorgestelde mitigerende en compenserende maatregelen dienen te worden uitgevoerd zoals omschreven in het “Projectplan voor de realisatie van Deelplan 1 van het project Meerstad” van 2007 met inachtneming van het onderstaande.
8. Vóórdat alle werkzaamheden zullen plaatsvinden, dienen de compensatiemaatregelen reeds te zijn uitgevoerd. De nieuwe nestkasten dienen geplaatst te worden op een geschikte locatie, dat wil onder andere zeggen binnen het huidige leefgebied van de soorten waarvoor de ontheffing geldt.
9. Kort vóórdat de werkzaamheden gestart worden, dient een ter zake kundige1 te controleren of de huidige verblijfplaats in gebruik is. Eventueel aangetroffen exemplaren van de steenmarter dienen te worden verjaagd of in de gelegenheid gesteld te worden de schuur te verlaten, waarna de verblijfplaats onaantrekkelijk of ontoegankelijk gemaakt dient te worden tot de werkzaamheden plaatsvinden, om hervestiging tussentijds te voorkomen.
10. Kort voordat de werkzaamheden gestart worden, dient een ter zake kundige1 te controleren of de huidige verblijfplaats in gebruik is. Bij een broedgeval mogen geen werkzaamheden worden verricht. Eventueel aangetroffen (niet-broedende) exemplaren dienen in de gelegenheid gesteld te worden om de schuur te verlaten, waarna de verblijfplaats onaantrekkelijk of ontoegankelijk gemaakt dient te worden tot de werkzaamheden plaatsvinden, om hervestiging tussentijds te voorkomen.
11. Een ter zake kundige1 dient bij alle maatregelen te worden betrokken.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[Hoofdweg 179 te Harkstede in de gemeente Slochteren.]]></location>
		<licensedJustification><![CDATA[Door de voorgenomen maatregelen zullen de volgende uilennesten verdwijnen:
·  Eén in 2005 voor het laatst gebruikte nestkast van een kerkuil en een in gebruik zijnde roestplaats van een steenuil in de grote schuur bij Heierhoeve;
·  Eén in 2006 gebruikte nestkast van een kerkuil in een paardenstal;
·  In de schuur op locatie (205,1x379,9) ten westen van de Annahoeve]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0123" userIdentity="Alterra1" derogation_reference="Alterra1-B-50-2009123116054452">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-07-01</licenseValidFrom>
		<licenseValidUntil>2008-09-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Omdat het onbekend was dat er steenuilen in het gebied aanwezig waren (ondanks het feit dat ecologisch onderzoek op voorhand was uitgevoerd in zowel 2005 als 2006), is het leefgebied inmiddels al dusdanig vernietigd dat behoud van de nestlocatie geen optie meer is. Als het steenuilenpaar immers in de huidige situatie toch zou besluiten te gaan broeden, dan zou de kans klein zijn dat de jongen het zouden overleven. In relatie hiermee is er dan ook vanuit de Zorgplicht (artikel 2 van de Flora- en faunawet) voor gekozen de nestlocatie vóór aanvang van het broedseizoen van de steenuil voor de soort ongeschikt te maken. Als vervanging voor deze locatie zijn enkele nestkasten in de omgeving opgehangen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.
Hoewel de bestemmingsplannen en de MER’s relatief globaal zijn opgesteld en niet tot op soortniveau doordringen, zijn naar mijn mening in de opgestelde plannen wel de meest waardevolle gebieden ontzien door de gemaakte keuzes in alternatieven. Hierdoor worden met betrekking tot vele beschermde soorten geen verbodsbepalingen overtreden en wordt schade zoveel mogelijk voorkomen. Een eerder voorgesteld alternatief voor de compensatie voor de kerkuil en de steenuil was geen optie, omdat het gelegen is in een gebied waar, in de nabije toekomst, een nieuwe bestemming wordt opgelegd ten nadele van het voortbestaan van de compensatie. Het project, waarvoor ontheffing wordt aangevraagd, is wel probleemoplossend. De nu geplande compensatie voor kerkuil en steenuil kan voor een langere periode duurzaam behouden worden.]]></alternativesAssessed>
		<activities>
			<activity code="81">Deliberate disturbance during the period of breeding</activity>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
6. De compensatie voor de steenuil dient te worden uitgevoerd conform hoofdstuk 6 van het bij de 
in Nederweert” van februari 2008, met inachtneming van het onderstaande.
7. In relatie tot het aangetaste leefgebied van de steenuil in het plangebied, dienen de groenstroken langs de A2 en de laanbeplanting langs de Randweg-Zuid en het kanaal gehandhaafd te blijven.
8. Het toekomstig beheer van het compensatiegebied dient te worden afgestemd op de ecologische randvoorwaarden die voor de instandhouding van de steenuil vereist zijn.
9. Het bovenstaande dient na raadpleging van en/of onder begeleiding van een ter zake kundige1 te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Pannenweg Nederweert" in de gemeente Nederweert]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0416" userIdentity="Alterra1" derogation_reference="Alterra1-B-52-2010010309352077">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-05-29</licenseValidFrom>
		<licenseValidUntil>2008-12-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[U geeft aan dat niet bouwen niet aan de orde is, omdat de gemeente een woningbouwopgave vanuit de landelijke overheid heeft. De gemeente Barneveld heeft de taak om zijn eigen bevolking op te vangen. Daarnaast heeft de gemeente een regionale taak voor bedrijfsterreinen vanuit het streekplan. Bovendien is de gemiddelde woningbezetting hoger dan het landelijk gemiddelde. Er zijn verschillende alternatieven aangedragen voor dit plangebied. U geeft aan dat de gemeente Barneveld ingeklemd zit tussen beken die fungeren als Ecologische Verbindingszone (EVZ) en bosrijke gebieden die geen mogelijkheden tot alternatief bieden voor woningbouw omdat ze zijn vastgelegd in de Ecologische Hoofdstructuur (EHS). In de zones aangewezen als natuur komen ten eerste hoge natuurwaarden voor en ten tweede zijn deze gebieden strategisch van groot belang voor natuurontwikkeling.
Daarnaast wordt inbreiding in bestaand bebouwd gebied al optimaal benut. Intensievere bebouwing zal leiden tot een vraag om meer ruimte, omdat er geen vraag is naar de hierbij behorende woningen waardoor de vraag naar woningen van het huidige type blijft bestaan. Hierdoor zal er dan ook meer ruimtebeslag komen, ten koste van het leefgebied van de steenuil.
Voor het onderhavige project wordt de verblijfplaats van de steenuil verplaatst, waardoor de gunstige staat van instandhouding op korte termijn niet in het geding komt. Het project, waarvoor ontheffing wordt aangevraagd, is daarom probleemoplossend. Het is voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
			<activity code="81">Deliberate disturbance during the period of breeding</activity>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Vóór de sloop van de gebouwen dienen in het compensatiegebied twee steenuilenkasten opgehangen te worden. Deze steenuilenkasten dienen met behulp van een ter zake kundige1 op het gebied van steenuilen op de meest gunstige locatie geplaatst worden.
8. De boerderij dient gesloopt te worden in de periode september tot en met eind november. In deze periode zijn de jongen uitgevlogen en is er nog geen nieuw legsel aanwezig.
9. Vóórdat het gebouw gesloopt kan worden, dient door een ter zake kundige1 op het gebied van steenuilen gekeken te worden of de steenuil niet in de schuur aanwezig is.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Burgemeester Labreelaan te Barneveld" in de gemeente Barneveld, gelegen aan de Burgemeester Labreelaan.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0474" userIdentity="Alterra1" derogation_reference="Alterra1-B-53-2010010309501513">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-01</licenseValidFrom>
		<licenseValidUntil>2009-03-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Strix aluco, Buteo buteo, Accipiter gentilis, Falco hanunculus]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Voor het project zijn verschillende inrichtingsalternatieven voorgesteld voor de toegangsweg en het boomkronenpad. Het huidig gekozen tracé is hiervoor het meest geschikt, voor gemotoriseerd verkeer en heeft meer voordelen ten opzichte van de twee andere tracéopties, bijvoorbeeld kortere toegangsweg en verkeersveiligheid. De keuze voor de beoogde locatie van het boomkronenpad is gebaseerd op het feit dat dit het enige bos is waarbinnen de aanleg van een dergelijk pad mogelijk is.
Er zijn, met betrekking tot de huidig gekozen locatie, geen alternatieve locaties beschikbaar die een betere bevredigende oplossing kunnen bieden voor de aanwezige beschermde soorten. Er zijn wellicht andere locaties denkbaar, maar deze veroorzaken mogelijk meer negatieve effecten op zwaar beschermde soorten dan de huidig gekozen locatie. Uit het bij de aanvraag gevoegde onderzoeksrapport “Toets Flora- en faunawet Natuur - en Recreatiepark Drakenrijk, gemeente Beesel” van 30 oktober 2007, blijkt namelijk dat er ten zuiden van de plangebieden dassen voorkomen en ten oosten van het plangebied steenuilen. Deze soorten ontbreken juist in het plangebied. Met betrekking tot de gekozen wegtracés en het boomkronenpad zijn er andere denkbare tracés mogelijk. Er gaan echter geen vaste nesten verloren in het bos en het grootste deel van het bos blijft intact. Bovendien zijn de alternatieven met betrekking tot de inrichting en/of werkwijze zo voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen, aantasting fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>4</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de bosuil, buizerd, havik en de torenvalk komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Alle compenserende en mitigerende maatregelen, genoemd op pagina 55 tot en met 59 van het bij de aanvraag gevoegde onderzoeksrapport “Toets Flora- en faunawet Natuur - en Recreatiepark Drakenrijk, gemeente Beesel” van 30 oktober 2007, dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1, met inachtneming van het onderstaande.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Natuur- en Recreatiepark Drakenrijk", gelegen ten zuiden van Reuver in de gemeente Beesel. Het plangebied omvat het landelijk gebied tussen de N567 (Broekweg), de N271 (Streekweg) en de kern Reuver]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0291" userIdentity="Alterra1" derogation_reference="Alterra1-B-54-2010010310050598">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-06-04</licenseValidFrom>
		<licenseValidUntil>2012-07-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[In de gemeente Rheden is de ruimte om te bouwen schaars, doordat het gebied tussen de beschermde Veluwe en het IJsseldal ligt. Om die reden worden uitsluitend inbreidingslocaties gezocht. De planlocatie vormt een van deze locaties. Buiten de nu vrijgekomen locatie Rheden Bestrating liggen in het dorp Rheden vrijwel geen reële woningbouwmogelijkheden.
De onderhavige keuze betreft een transformatie van bedrijventerrein naar woningbouwlocatie, die aansluit op de bestaande bebouwing en het centrum van het dorp.
Inrichting en werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen. De gunstige staat van instandhouding blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen met nest- en roestplaats</method>
		</methods>
		<reasons>
			<reason code="FT">uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de kerkuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Er dient voor de kerkuil tijdelijke compensatie te worden gerealiseerd van nest- en roestgelegenheid (kasten), op het terrein van de gemeentewerf. Deze dient klaar te zijn vóórdat de gebouwen waarin zich de kerkuilen momenteel bevinden, worden gesloopt.
8. Definitieve compensatie van broed- en roestgelegenheid voor kerkuilen dient te worden gerealiseerd binnen en buiten het plangebied. Binnen het plangebied dienen kasten in een overdekte, beschutte constructie aan de nieuwe hoogbouw geplaatst worden. Buiten het plangebied dienen tenminste twee kasten op een geschikte locatie, in samenwerking met de plaatselijke kerkuilenwerkgroep geplaatst te worden.
9. De definitieve compensatie voor kerkuilen buiten het plangebied moet ruim vóórdat de gemeentewerf gesloopt wordt, geschikt zijn.
10. Voorafgaand aan de sloopwerkzaamheden dient een controle plaatsvinden door een ter zake kundige1 op het gebied van de kerkuil, waarbij vastgesteld dient te worden of er kerkuilen aanwezig zijn. Indien er broedgevallen aanwezig zijn, dient met de werkzaamheden te worden gewacht totdat de laatste jongen zijn uitgevlogen. Indien alleen volwassen en vliegvlugge jongen aanwezig zijn, dienen deze voorafgaand aan de werkzaamheden te worden verjaagd.
11. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van kerkuilen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Rheden Bestrating" in de gemeente Rheden; Groenestraat, de Dr. Langenmeyerweg, de Pinkelseweg en de Veerweg]]></location>
		<licensedJustification><![CDATA[Door de voorgenomen maatregelen zullen de volgende uilennesten verdwijnen:
·  Eén in 2005 voor het laatst gebruikte nestkast van een kerkuil en een in gebruik zijnde roestplaats van een steenuil in de grote schuur bij Heierhoeve;
·  Eén in 2006 gebruikte nestkast van een kerkuil in een paardenstal;
·  In de schuur op locatie (205,1x379,9) ten westen van de Annahoeve]]></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0111" userIdentity="Alterra1" derogation_reference="Alterra1-B-55-2010010310253227">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-06-04</licenseValidFrom>
		<licenseValidUntil>2010-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL13">Drenthe</region>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Voor de voorgenomen kadeversterking is geen alternatieve oplossing denkbaar. Voor de stabiliteit van de opgehoogde kade moet er een talud direct langs de kade worden gelegd, hiervoor zijn geen alternatieve locaties aanwezig of alternatieve werkwijzen mogelijk.
De periode van uitvoering is afgestemd op de minst kwetsbare periode van de aanwezige beschermde soorten.
De werkzaamheden zijn locatiegebonden; een onderzoek naar alternatieve locaties is daarom niet aan de orde. Er is voldoende rekening gehouden met de aanwezige beschermde soorten. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="41">For the protection of wild flora</reason>
			<reason code="42">For the protection of wild fauna</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De ontheffinghouder dient bij de planning van de werkzaamheden rekening te houden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (voortplanting, winterrust) te voorkomen.
8. De werkzaamheden dienen uitgevoerd te worden conform de voorgestelde methode, beschreven in de paragrafen 3.1 en 3.2 in het bij de aanvraag gevoegde rapport ‘Projectomschrijving ten behoeve van ontheffingsaanvraag ex. Art. 75 Flora- en Faunawet’ van 13 februari 2008, met inachtneming van onderstaande voorwaarden.
14. Vóór de aanvang van kapwerkzaamheden dienen (potentiële) nestbomen van de grote bonte specht te worden gecontroleerd door een ter zake kundige1 op het gebied van vogels, op de aanwezigheid van vogels in de holtes. Eventueel aanwezige exemplaren dienen te worden verjaagd.
15. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.
16. Bovenstaande mitigerende maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Kadeversterking ‘Kromme Mijdrecht - De Hoef’" in gemeenten Uithoorn, De Ronde Venen en Liemeet]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0088" userIdentity="Alterra1" derogation_reference="Alterra1-B-56-2010010310430133">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-06-12</licenseValidFrom>
		<licenseValidUntil>2013-03-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis, Dendrocopos major]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Op 25 november 2002 heeft het College van de gemeente Tilburg ingestemd met de marktvisie voor de locatie Stappegoor. Het doel van de herinrichting van het plangebied is het versterken van activiteiten voor sport, onderwijs en vrijetijdsbesteding. Er is een component wonen aan de inrichting van het gebied toegevoegd om de exploitatie rond te krijgen. Er zijn mogelijkheden onderzocht om (delen van) de bomenrijen in te passen in de nieuwe inrichting van het plangebied. Er zijn echter minimumoppervlakten vastgesteld die noodzakelijk zijn voor de te realiseren functies. Daarbij moeten de functies aansluiten op de huidige inrichting van het gebied, zodat nieuwe sportvelden naast de huidige sportvelden komen te liggen en de nieuwe woningen bij de huidige bebouwing. Om deze redenen is het niet mogelijk om de bomenrijen met de nestholtes te behouden.
Ecologisch gezien zou het sparen van de bomenrijen niet bijdragen aan een duurzaam behoud van de nestholtes van de groene specht en de grote bonte specht, omdat het gebruik van het terrein wordt geïntensiveerd na afronding van de ingreep. Het is de vraag of de nestholtes dan nog wel gebruikt zouden worden. Daarnaast is de voorgestelde werkwijze dusdanig, dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding gewaarborgd blijft. Ook zijn er in de omgeving voldoende uitwijkmogelijkheden voor beide spechtsoorten aanwezig. Hiermee is het voldoende aangetoond dat voor het project geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezende uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht  en de  grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen dienen uitgevoerd te worden zoals beschreven op pagina 7 van het bij de ontheffingsaanvraag gevoegde rapport ‘Onderbouwing ontheffingsaanvraag Flora – en faunawet Herinrichting Stappegoor Tilburg’ van 6 februari 2008, met in achtneming van de onderstaande voorwaarde.
8. Direct voorafgaand aan de kapwerkzaamheden dienen de te kappen bomenrijen geïnventariseerd te worden op de aanwezigheid van de groene specht en de grote bonte specht. Dit dient te gebeuren onder begeleiding van een ter zake kundige1. Indien er holtes in gebruik zijn, dient met een ter zake kundige1 overlegd te worden welke werkwijze gehanteerd dient te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Herinrichting Stappegoor Tilburg" in de gemeente Tilburg; in het zuiden van Tilburg, grofweg tussen de Goirlese weg, Ringbaan Zuid, Stappegoorweg en de A58]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0382" userIdentity="Alterra1" derogation_reference="Alterra1-B-57-2010010311034514">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-07-01</licenseValidFrom>
		<licenseValidUntil>2009-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De omliggende gebieden zijn niet beschikbaar als uitbreidingsgebied voor de golfbaan, het gekozen gebied is de enige beschikbare optie. Uitbreiding richting het oosten of het westen is niet mogelijk vanwege de bestaande bebouwing en infrastructuren. Het terrein ten zuiden van het plangebied is in het streekplan aangewezen als Milieubeschermingsgebied voor stilte. Uitbreiding richting het zuiden is daarom ook niet mogelijk. Door de uitvoering van de werkzaamheden is sprake van verstoring en afname van het leefgebied van de beschermde soorten. Dit is echter tijdelijk. Door het aanleggen van nieuwe wateren met natuurvriendelijke oevers, die in verbinding komen te staan met de bestaande wateren, zal het leefgebied voor de bittervoorn en de kleine modderkruiper uiteindelijk worden uitgebreid. Het project is probleemoplossend. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
			<activity code="81">Deliberate disturbance during the period of breeding</activity>
		</activities>
		<methods>
			<method code="FT">aantasting fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de aanwezige beschermde soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare periode (voortplanting) te voorkomen.
8. Met betrekking tot de steenuil dienen de compenserende maatregelen uitgevoerd te worden zoals deze beschreven zijn in het bij de aanvraag gevoegde rapport “Compensatieplan uitbreiding Golfbaan Delfland, Schipluiden” van 30 april 2008.
9. Ten einde de kwaliteit van het compensatieterrein als foerageerlocatie te waarborgen, dient jaarlijks monitoring plaats te vinden van het gebruik. Het monitoren dient te gebeuren voor een periode van drie jaar en dient te starten na voltooiing van het compensatieplan. De monitoringsresultaten dienen te worden geanalyseerd, mede in relatie tot historische gegevens. Deze analyse dient jaarlijks aan Dienst Regelingen te worden aangeleverd onder vermelding van ‘FF/75C/2007/0382’. Zonodig kunnen aanvullende maatregelen worden bepaald.
10. De mitigerende maatregelen dienen te worden uitgevoerd zoals is vermeld in het bij de aanvraag gevoegde rapport “Natuurtoets Golfbaan Delfland, Schipluiden”, van 10 september 2007. Uitzondering hierop zijn de vermelde voortplantingsperiodes van de bittervoorn en de kleine modderkruiper. Globaal loopt de periode van voortplanting voor de bittervoorn van april tot en met augustus en voor de kleine modderkuiper van maart tot en met augustus. In deze perioden mogen geen werkzaamheden worden uitgevoerd. Afhankelijk van de weersomstandigheden kan deze periode langer dan wel korter zijn. Dit dient door een ter zake kundige1 te worden bepaald.
13. Alle bovenstaande maatregelen en maatregelen genoemd in de bovengenoemde rapporten dienen te worden uitgevoerd onder begeleiding van een ter zake kundige op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Uitbreiding Golfbaan Delfland" in de gemeente Schipluiden, gelegen ten noorden van Schipluiden tussen de kruising van de A4 en de Rijkswegstraat,]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0107" userIdentity="Alterra1" derogation_reference="Alterra1-B-58-2010010311125842">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-01</licenseValidFrom>
		<licenseValidUntil>2011-06-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Strix aluco]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De Rijksweg N34 gaat momenteel door Ommen heen. Dit levert allerlei problemen op. De nieuwe autoweg (doortrekken van de N36) biedt een oplossing voor de verkeersproblemen op de bestaande N34. Het verkeer richting centrum Ommen kan niet goed doorrijden.
Vooral in de spits ontstaan hierdoor files en onveilige verkeerssituaties. Omwonenden hebben last van het geluid en stank van het verkeer. Daarnaast verbetert het hoofdwegennet tussen Twente en Noord-Nederland en de regionale verbinding tussen Hardenberg en Zwolle. In de MER die in 2000 is verschenen is een groot aantal tracés onderzocht, waarbij ook de milieuaspecten van de verschillende oplossingen in beeld zijn gebracht.
Hierbij is rekening gehouden met eisen vanuit verkeersveiligheid, het leveren van een verantwoorde inpassing in het landschapspatroon en met de beleving van het landschap door de bewoners en weggebruikers. Het voorliggende tracé is gekozen als beste optie door de Minister van Verkeer en Waterstaat in samenspraak met de Minister van Volkshuisvesting, Ruimtelijke Ordening en Milieubeheer. De voorgestelde mitigerende en compenserende maatregelen voor dit tracé leiden ertoe dat de gunstige staat van instandhouding voor de verschillende beschermde soorten niet in het geding komt. Het project biedt een bevredigende oplossing. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">Schuur slopen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de bosuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
13. De sloop van het schuurtje dient pas uitgevoerd te worden wanneer duidelijk is dat de bosuil niet aanwezig is. Dit moet door een ter zake kundige1 op het gebied van uilen bekeken worden.
14. In overleg met een ter zake kundige1 op het gebied van uilen dienen in de omgeving van het schuurtje voor de bosuil twee kasten opgehangen te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Omleiding Ommen N34/N36". Het gedeelte van het tracé betreffende de Omleiding is gelegen tussen de N48 en de Witte Paal (Rijksweg 36)]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0031" userIdentity="Alterra1" derogation_reference="Alterra1-B-59-2010010313232811">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-07-15</licenseValidFrom>
		<licenseValidUntil>2010-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[De opstallen in het plangebied bevinden zich, met uitzondering van de kapschuur, in zeer bouwvallige staat en leveren daarom gevaar op. Om die reden zijn de opstallen, met uitzondering van de kapschuur, op last van de gemeente Barneveld al gesloopt. Het is onduidelijk of hier beschermde soorten aanwezig waren. Voor de aanwezige beschermde soorten zijn de meeste effecten te verwachten bij de sloop van de kapschuur. De sloop van de opstallen is uiteraard locatiegebonden en hiervoor zijn geen alternatieven. De inrichting en werkwijze zijn zodanig voorgesteld, dat verdere verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding verder gewaarborgd blijft.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen met nestplaats</method>
		</methods>
		<reasons>
			<reason code="FT">uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de kerkuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Binnen twee weken na datum ontheffingverlening, dienen vier steenuilenkasten in de bomen binnen het plangebied te worden opgehangen.
8. Na de voltooiing van de nieuwbouw dient in één van de bijgebouwen een kerkuilenkast te worden opgehangen. Pas hierna én wanneer gecontroleerd is dat de kerkuil niet aan het broeden is of geen jongen heeft, dient de kapschuur te worden gesloopt.
9. Alle bovenstaande compenserende en mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van uilen.
10. Bromadiolon dient als enige bloedverdunnende stof ingezet te worden bij eventuele knaagdierbestrijding. Andere bloedverdunnende stoffen (difethialon en brodifacoum) dienen niet ingezet te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Landgoed Groot Grevengoed", gelegen in Zwartebroek, gemeente Barneveld aan de Koperweg 2 met postcode 3785 KN.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0559" userIdentity="Alterra1" derogation_reference="Alterra1-B-60-2010010313413145">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-08-15</licenseValidFrom>
		<licenseValidUntil>2009-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De slachterij is in verval geraakt en dient gesaneerd te worden. Daarom moet de bebouwing op het terrein gesloopt worden. De herontwikkeling van het plangebied staat niet op zichzelf, maar maakt deel uit van de integrale ‘Gebiedsvisie Wesepe, kansen en kaders’ die door de gemeenteraad van de gemeente Olst-Wijhe is vastgesteld. Kern van de visie is het inspelen op de verlegging van de provinciale weg (N348) die langs het westen van Wesepe wordt omgeleid. Op verschillende locaties wordt de wegverlegging gekoppeld aan het ontwikkelen van bedrijven en woningen. Om verdere verstening van het landelijk gebied te beperken is de locatie van de slachterij gekozen. Er is geen ander alternatief afgewogen, waarbij de betreffende soorten minder in het geding zouden kunnen komen.
Het gebouw voldoet door de functionele en bouwtechnische veroudering niet meer aan de huidige eisen. Er worden voldoende compenserende en mitigerende maatregelen getroffen, waardoor de gunstige staat van instandhouding van de steenuil niet door de
werkzaamheden in het geding zal komen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouw</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Vóórdat tot sloop wordt overgegaan, dient door een ter zake kundige1 te worden vastgesteld of in het te slopen gebouw op dat moment geen nesten met eieren of nestgebonden jongen aanwezig zijn of dat de steenuilen broedgedrag vertonen. Bij dergelijke constateringen dient de sloop uitgesteld te worden, totdat de (jonge) steenuilen het nest verlaten hebben.
8. Indien blijkt dat er geen bewoond nest aanwezig is, dient de dakrand voorzichtig gedemonteerd te worden.
9. De sloopwerkzaamheden dienen buiten de periode april tot en met half augustus plaats te vinden.
10. De derde nestkast dient vóór half augustus binnen het plangebied opgehangen te worden. Hierbij dient een ter zake kundige1 betrokken te worden.
11. De twee nestkasten die reeds opgehangen zijn aan de Mengerweg, en de nog te plaatsen nestkast binnen het plangebied, dienen regelmatig gecontroleerd te worden door een ter zake kundige1.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Vervangende nieuwbouw slachterij Wesepe" in de gemeente Olst-Wijhe; Boxbergerweg 63]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0103" userIdentity="Alterra1" derogation_reference="Alterra1-B-61-2010010313511595">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-07-24</licenseValidFrom>
		<licenseValidUntil>2010-06-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL34">Zeeland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het plan om de Hans Vriezenschans te reconstrueren en beleefbaar te maken vloeit voort uit de aanwijzing van het gebied als onderdeel van het Nationaal Landschap Zuidwest Zeeland. De Staats Spaanse Linies vormt de ruggengraat van dit nationale landschap. Sturend bij de planvorming is de geschiedenis/ archeologie. Het project is daarom locatiegebonden.
Alternatieve locaties zijn uitgesloten. In relatie tot de aanwezige restanten van dit onderdeel van de Staats Spaanse Linies, is voor de locatiekeuze voldoende aannemelijk gemaakt dat voor de reconstructie geen alternatieve locaties aanwezig zijn. Voor wat betreft de inrichtingsalternatieven zijn 5 alternatieven uitgewerkt, waarbij uiteindelijk is gekozen voor een compromis; een gedeeltelijke reconstructie van het object Hans Vriezenschans, waarbij enkele essentiële onderdelen van het gebied voor de aanwezige soorten behouden kunnen blijven, in combinatie met mitigerende en compenserende maatregelen die zijn afgestemd op waarborging van de ter plaatse voorkomende soorten. Indien op adequate wijze uitgevoerd, kan hiermee de gunstige staat van instandhouding van de lokale populatie worden gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="T002">Moving motor vehicles</method>
			<method code="FT">aantasting leefgebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De werkzaamheden dienen conform de compenserende en mitigerende maatregelen genoemd in paragrafen 3.5, 3.7 en 4.6 en 4.7 van het bij de aanvraag gevoegde rapport ‘Ecologische analyse ten behoeve van toetsing van de inrichting Hans Vriezeschans aan de natuurwetgeving’ van november 2007 en zoals nader verklaard in de aanvullende informatie van 15 en 16 april 2008, te worden uitgevoerd.
8. De werkzaamheden dienen zodanig gepland worden dat er ten tijde van de werkzaamheden altijd minimaal 0,25 hectare ruig grasland in het plangebied beschikbaar is, buiten de (directe) invloedssfeer van de voorgenomen werkzaamheden.
9. Tijdens de uitvoering dient zoveel mogelijk achteruit gewerkt te worden en er dient gewerkt te worden met zo min mogelijk werkpaden.
10. Er dient niet gewerkt te worden in de periode van februari tot en met augustus om de voortplantingsperiode van de veldspitsmuis en de steenuil te ontzien. Voorts dient specifiek te worden bepaald wanneer de voortplantingstijd van het betreffende steenuilpaartje aanvang vindt en eindigt en waar eventuele jongen zich vestigen. Indien eventuele jongen van de steenuil zich vestigen in de buurt van de werkzaamheden dienen aanvullende maatregelen te worden getroffen.
13. De voormalige boomgaard en verwilderde tuin aan de oostkant van het terrein dienen te worden ontzien. Ook dienen uitsluitend die bomen en struiken verwijderd te worden die voor de inrichtingswerkzaamheden strikt noodzakelijk zijn. Voorts dient de nestboom van de steenuil duurzaam behouden te blijven.
14. Om de rust in het gebied te behouden, dient recreatief gebruik van het gebied beperkt te blijven tot de oostzijde van gebied.
15. Het toekomstig beheer van het gebied dient te worden afgestemd op de ecologische randvoorwaarden die voor de instandhouding van zowel de veldspitsmuis, als de steenuil vereist zijn.
16. Het bovenstaande dient door, na raadpleging van en/of onder begeleiding van een ter zake kundige1 te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Staats Spaanse Linies, object Hans Vriezenschans" in de gemeente Sluis; de oude Haven 46 te Oostburg]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0215" userIdentity="Alterra1" derogation_reference="Alterra1-B-62-2010010314000781">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-07-21</licenseValidFrom>
		<licenseValidUntil>2008-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL32">Noord-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De nieuwe Stichtseweg wordt een gebiedsontsluiting van de nieuwe wijk De Blaricummermeent. De nieuwe Stichtseweg zal het herkomst- en bestemmingsverkeer van- en naar de A27 ontsluiten. Hierbij wordt gebruik gemaakt van de ligging van de huidige Stichtseweg. Dit is de enige mogelijkheid tot ontsluiting van de nieuwe woonwijk waarbij gebruik wordt gemaakt van de huidige infrastructuur (met aanpassing) zonder grootschalige ingrepen elders of overlast in huidige woonkernen te veroorzaken. U heeft
geen alternatieven onderzocht.
Het betreft echter een uitbreiding van de bestaande weg, het is derhalve zeer aannemelijk dat de aanleg van een nieuwe weg op een andere locatie een grotere ingreep voor aanwezige soorten zou betekenen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="41">For the protection of wild flora</reason>
			<reason code="42">For the protection of wild fauna</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Gedurende de werkzaamheden dient rekening gehouden te worden met het broedseizoen van de grote bonte specht. Verstoring van broedgevallen dient te worden voorkomen. Werkzaamheden dienen buiten de broedperiode van aanwezige soorten uitgevoerd te worden. Ik wijs u erop dat voor het broedseizoen geen standaardperiode wordt gehanteerd in het kader van de Flora- en faunawet. Van belang is of een broedgeval verstoord wordt, ongeacht de periode. Het einde van het broedseizoen dient te worden vastgesteld door een ter zake kundige1 op het gebied van vogels.
8. Vóór aanvang van de kapwerkzaamheden dienen, door een ter zake kundige1 op het gebied van vogels, bomen met een nest- of verblijfplaats van de grote bonte specht te worden gecontroleerd op de aanwezigheid van vogels. Indien bewoning is uitgesloten, kunnen kapwerkzaamheden uitgevoerd worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Reconstructie Stichtseweg" en betreft de Stichtseweg, gelegen in de gemeente Blaricum]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0237" userIdentity="Alterra1" derogation_reference="Alterra1-B-63-2010010314062045">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-08-08</licenseValidFrom>
		<licenseValidUntil>2010-03-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De wilgen langs het fietspad verkeren niet in optimale staat. In eerste instantie was het uitgangspunt bij de planvorming dat de wilgen naast het fietspad behouden zouden blijven. Gezien de ouderdom van de bomen en de toename van het gebruik van het fietspad is besloten om een boomeffectenanalyse uit te voeren. In dit onderzoek is geconcludeerd dat de toekomstverwachting van de bomen 6 tot 10 jaar is. De houtstructuur is matig tot slecht en er is verhoogde kans op takbreuk, waardoor de veiligheid van de fietsers in het geding komt. Mede vanuit veiligheidsoverwegingen is besloten om bomenrijen langs het fietspad te kappen. Vanwege de conditie waarin de bomen verkeren en de beperkte toekomstverwachting van de bomen is er niet gekozen voor het alternatief waarbij de bomen geknot of gesnoeid zouden worden. Ten aanzien van de grote bonte specht zou het beter zijn om wel voor dit alternatief te kiezen. In de omgeving is echter voldoende alternatief leefgebied voor de soort aanwezig, waardoor de gunstige staat van instandhouding van de grote bonte specht niet in het geding komt. Daarnaast worden er voldoende mitigerende en compenserende maatregelen getroffen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="T002">Moving motor vehicles</method>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen dienen uitgevoerd te worden zoals beschreven staat op pagina 23 van het bij de aanvraag gevoegde “Projectplan Park Lagewei Gemeente Barendrecht” van 10 april 2008.
8. Alle mitigerende maatregelen dienen uitgevoerd te worden onder begeleiding van een ter zake kundige1 op het gebied van vogels. Indien er bij de controle in gebruik zijnde nesten van de grote bonte specht worden aangetroffen, dient de ter zake kundige1 de omvang van de rustzone te bepalen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Park Lagewei" en betreft de directe omgeving van het fietspad dat van zuid naar noord is gelegen tussen de Kilweg en de Middeldijk in de gemeente Barendrecht]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0056" userIdentity="Alterra1" derogation_reference="Alterra1-B-64-2010010314293019">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-01</licenseValidFrom>
		<licenseValidUntil>2013-09-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[U heeft twee alternatieve manieren aangedragen om het plangebied in te richten, te weten het basisalternatief en het meest milieuvriendelijke alternatief. In beide alternatieven vormt het plangebied een nieuwe ecologische schakel tussen de Dordwijkzone en het buitengebied. De vernietiging van een deel van het territorium en het foerageergebied van de steenuil is tijdelijk. Er worden voldoende maatregelen genomen om het gebied na realisatie van het project weer geschikt te maken als territorium en foerageergebied voor de steenuil. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing
voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">aantasting leefgebied</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Ter compensatie van het verloren gaan van territorium en foerageergebied van de steenuil dienen inrichtings- en beheersmaatregelen genomen te worden zodat het plangebied na voltooiing opnieuw geschikt is voor de steenuil. De inrichtings- en beheersmaatregelen dienen opgenomen te worden in een inrichtings- en beheersplan. Dit plan dient voordat de werkzaamheden van start gaan goedgekeurd te zijn door Dienst Regelingen.
8. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de steenuil.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Belthurepark, Golf en Wonen" aan de Stevensweg 40 in de gemeente Dordrecht; gebied begrensd door Oudendijk, het Laantjes van Middenhoeve, de Zuidendijk en de Meeuwenseweg, de Zeedijk en de Schenkeldijk, Zuidendijk en de Stevensweg.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0086" userIdentity="Alterra1" derogation_reference="Alterra1-B-65-2010010314404614">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-01</licenseValidFrom>
		<licenseValidUntil>2009-09-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Om te voorzien in de woningbehoefte in de gemeente Ermelo dient de woningvoorraad op peil te blijven en enigszins te worden uitgebreid. Op deze wijze kan voorzien worden in een diversiteit in woningen in verschillende categorieën ten behoeve van diverse doelgroepen van volkshuisvestingsbeleid. Naast enkele andere projecten in de gemeente is dit project noodzakelijk om structureel te voorzien in die behoefte. Daarnaast genereert dit project financiële middelen om te investeren in andere onrendabele woningprojecten elders in de gemeente. Met dit project wordt tevens voldaan aan de afspraken die tussen de provincie Gelderland en de regio Noord-Veluwe zijn gemaakt inzake aantallen en categorieën woningbouw. De kern van de gemeente Ermelo wordt aan de oost-, west-, en zuidzijde begrensd door Natura 2000-gebieden, landbouw-intensiveringsgebied, recreatiegebieden of open landschappelijk waardevolle weidegebieden. Aan de noordzijde van het plangebied liggen bedrijventerreinen.
Het plangebied sluit aan bij de bebouwing van de bestaande woonkern en vormt een buffer ten opzichte van de noordelijk gelegen bedrijventerreinen. Om die reden is de omzetting van deze camping en bungalowpark in een woonwijk, met als thema ‘wonen in een parkbos, te gast in het landschap’, een logische en verantwoorde keuze. Er zijn derhalve geen goede alternatieven voorhanden. Getracht wordt het bosbiotoop en het karakter van het gebied zoveel mogelijk te behouden en te versterken in de aanliggende (bosen park)gebieden. De inrichting en werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="T002">Moving motor vehicles</method>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
8. Voorafgaand aan de kap dienen aanwezige grote bonte spechten verjaagd te worden uit het nest (kloppen op de betreffende boom). De kap kan plaatsvinden nadat door een ter zake kundige1 is vastgesteld dat er zich geen jongen meer in het nest bevinden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Trefpunt, Ermelo"; Kalkoenweg, de Prins Hendriklaan, de provinciale weg N303 (Harderwijkseweg) en de Hoenderweg]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0281A" userIdentity="Alterra1" derogation_reference="Alterra1-B-72-2010011213340079">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2009-01-01</licenseValidFrom>
		<licenseValidUntil>2013-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Aan de hand van de MER is het beste alternatief bepaald en dit is vervolgens opgenomen in het bestemmingsplan van de gemeente Deurne. Ten aanzien van meerdere locaties zijn verschillende criteria beschouwd, waaronder ‘biotoopverlies flora en fauna’, ‘beïnvloeding ecologische relaties’, ‘verstoring’ en ‘lichthinder natuurgebieden’. Aan het eerstgenoemde criterium is daarbij het meeste gewicht toegekend. U geeft aan dat de alternatievenafweging heeft plaatsgevonden op basis van een habitatgeschiktheidsanalyse van verschillende soortgroepen, die vergelijkbaar zou zijn met een quick-scan voor de Floraen faunawet. De huidige gekozen locatie (in de MER aangeduid als ‘locatie 2’) komt in de MER met betrekking tot de effectenbeschrijving ten opzichte van het criterium ‘biotoopverlies flora en fauna’ als meest gunstige naar voren. Er wordt vermeld dat de habitatgeschiktheid van deze locatie relatief laag is en dat er hier relatief weinig soorten zouden voorkomen. Dit wordt bevestigd door nader veldonderzoek ten aanzien van het gekozen alternatief. Het huidige plangebied wordt gekenmerkt door agrarisch gebruik (grote open ruimten) en betreft hoofdzakelijk veehouderijen. Ten aanzien van voornoemd ruimtegebruik en de uitgevoerde analyse, acht ik een dergelijke werkwijze voldoende om met betrekking tot de alternatievenafweging, tot een verantwoorde locatiekeuze te komen.
Ten aanzien van de verdere uitwerking van het gekozen alternatief is er onder meer voor gekozen het aanwezige lanenpatroon in het gebied, waaraan grote waarden worden toegekend, zoveel mogelijk in het plan te implementeren. Voorts bent u voornemens ten aanzien van de uitvoering van de werkzaamheden in het huidige plangebied zorgvuldig te handelen. Ik ben op grond van het bovengenoemde van mening dat het voorgenomen project ten aanzien van voorkomende (beschermde) soorten bevredigend tot een einde wordt gebracht. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">laanboom kappen</method>
		</methods>
		<reasons>
			<reason code="FT">De uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
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			<individuals>0</individuals>
			<eggs>0</eggs>
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			<individuals>0</individuals>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het verwijderen van de betreffende nestboom van de grote bonte specht dient plaats te vinden buiten de broedperiode van de soort. Aangezien er geen standaard broedperiode is, dient de betreffende boom voorafgaande aan het kappen daarvan door een ter zake kundige1 op de aanwezigheid van de grote bonte specht te worden gecontroleerd. Indien het nest in gebruik is, dient met kappen gewacht te worden tot de jongen zijn uitgevlogen.
8. De laanbomen in het plangebied, die zich bevinden langs bestaande, te handhaven infrastructuur, dienen zoveel mogelijk te worden behouden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Dit betreft een verlenging van de ontheffing FF/75C/2007/0281
Ik zie op ecologische gronden geen belemmeringen om de ontheffingsperiode ten aanzien van de verleende ontheffing te verlengen tot 31 december 2013. Aangezien er zich in de tussenliggende periode geen wezenlijke wijzigingen hebben voorgedaan, is aanpassing van de ontheffingsvoorwaarden niet noodzakelijk. Verlenging van de oorspronkelijk ontheffing tot 31 december 2013 kan derhalve plaatsvinden conform de oorspronkelijke voorwaarden.

Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[Projectvestiging glastuinbouw Deurne,]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<species><![CDATA[Buteo buteo]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[De aanleg van de sportaccommodatie is een onderdeel van het Masterplan Maurik. In het masterplan is een afweging gemaakt tussen de diverse ruimtelijke opties. De belangrijkste conclusie in het masterplan is dat de concentratie op ‘Oost’ en een gefaseerde aanpak van de verbeterde ontsluiting de meest kansrijke combinatie is. Er is extra aandacht gegeven aan het water en de maatschappelijke haalbaarheid van het plan. Naast de ontwikkeling van het bedrijventerrein en de sportlocatie worden binnen het plangebied een verbindingsweg en een woningbouwlocatie gerealiseerd. Om op deze ontwikkelingen aan te sluiten en tevens voldoende ruimte te bieden voor natuur en water is ruimtelijk gezien de gekozen sportaccommodatie de meest voor de hand liggende. Inrichting en werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">omhakken nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
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		<selectiveBasis></selectiveBasis>
		<licensed>
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		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het verwijderen van het buizerdnest dient plaats te vinden wanneer het duidelijk is dat het nest buiten gebruik is. Dit dient door een ter zake kundige1 beoordeeld te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Aanleg sportaccommodatie Maurik" in de gemeente Buren, begrensd door de Driesweg en de Maurikse Wetering.]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<licenseValidUntil>2010-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Dendrocopus major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het doorgaande verkeer op de Stougjesdijk veroorzaakt problemen op het gebied van leefbaarheid, verkeersveiligheid, bereikbaarheid en doorstroming van het verkeer. Er is geconcludeerd dat deze problemen opgelost kunnen worden door het aanleggen van een nieuwe weg. Het project is voor een groot deel locatiegebonden, er moet immers een oplossing komen in de buurt van de Stougjesdijk. Er is een Tracénota / Milieueffectrapportage opgesteld waarin vier tracés beoordeeld zijn op hun milieueffecten. Alternatief 1 is afgevallen doordat de visuele hinder en geluidshinder te groot waren. Alternatief 4 sluit niet aan op de toekomstvisie van de gemeente Oud-Beijerland en heeft belangrijke negatieve effecten op het vlak van natuur, landschap, woon- en leefmilieu. Alternatieven 2 en 3 bleken de meest kansrijke alternatieven. Het alternatief met de minste milieugevolgen van deze twee, alternatief 3, is vervolgens als basis meegenomen voor het Meest Milieuvriendelijke Alternatief. Dit alternatief is vervolgens verder uitgewerkt tot het huidige plan.
Alternatieve oplossingen ten aanzien van de aanwezige beschermde soorten zijn niet overwogen. Door het uitvoeren van de voorgestelde mitigerende maatregelen wordt echter zorgvuldig gehandeld en de gunstige staat van instandhouding van de beschermde soorten komt niet in het geding door de voorgenomen werkzaamheden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
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		<licensed>
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			<eggs>0</eggs>
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			<otherType></otherType>
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			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
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			<otherType></otherType>
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		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd en de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de werkzaamheden dient rekening te worden gehouden met de seizoensactiviteiten van de buizerd en de grote bonte specht, om verstoring in de kwetsbare periode (voortplanting) te voorkomen.
8. Vóórdat de bomen met de nesten of nestholtes gekapt worden, dient gecontroleerd te worden of deze op dat moment gebruikt worden door een buizerd of een grote bonte specht. Eventuele aanwezige exemplaren dienen verjaagd te worden.
9. Alle bovenstaande maatregelen dienen uitgevoerd te worden onder begeleiding van een ter zake kundige1 op het gebied van vogels.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "‘N217 omleiding Stougjesdijk"; Stougjesdijk 290, 3261 KW, in de gemeente Oud-Beijerland]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-08-27</licenseValidFrom>
		<licenseValidUntil>2013-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project is locatiegebonden. Een verschuiving van het plan naar het oosten is niet mogelijk vanwege de spoorlijn, het kanaal Almelo en omdat het gebied al tegen de gemeente Twenterand ligt. Een verschuiving naar het westen is niet mogelijk in verband met de Veeneleiding, de bestaande woonkern Wierden, recreatiegebied ’t Lageveld en omdat het gebied al tegen de gemeentegrens met Wierden ligt. Verschuiving in noordelijke richting is niet mogelijk omdat het gebied al tegen de gemeentegrens met gemeente Twenterand ligt. Verschuiving in zuidelijke richting kan niet vanwege het bestaande bedrijvenpark Twente Zuid. Verkleining van het bedrijventerrein is ook geen optie, omdat daardoor exploitatie onrendabel wordt. De inrichting en werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">omhakken nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
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			<nests>1</nests>
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			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
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			<otherNumber>0</otherNumber>
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		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Tijdens het broedseizoen van de buizerd dienen er geen werkzaamheden te worden uitgevoerd voor het bouwrijp maken van het terrein op de projectlocatie.
8. Wanneer er tijdens de bouwwerkzaamheden in het plangebied een broedsel van de buizerd wordt aangetroffen, mag er geen verstoring plaatsvinden. Het nest dient in dat geval zoveel mogelijk te worden ontzien. De wijze waarop dat gebeurt dient in overleg met een ter zake kundige1 op het gebied van vogels te worden bepaald.
9. Het foerageergebied dient na het bouwrijp maken in stand te worden gehouden door middel van verruiging van het terrein en door beheer (aangepast maaibeheer, geen gebruik van meststoffen en geen gebruik van bestrijdingsmiddelen) van het terrein.
10. Bij aanleg van de landschappelijke groenstructuur op de noordrand van de projectlocatie dienen nieuwe bomen en/of boomgroepen aangeplant te worden als nieuwe (potentiële) nestlocaties. Deze compenserende maatregel dient in dezelfde periode plaats te vinden als het bouwrijp maken van het bedrijventerrein.
11. Alle bovenstaande werkzaamheden dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Bedrijvenpark Twente Noord (oost)" in de gemeente Almelo; Iepenweg Noord, Woestenweg en de edrijvenparksingel]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-01</licenseValidFrom>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis, Dendrocopos major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezende uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
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			<individuals>0</individuals>
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			<nests>2</nests>
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			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht  en de  grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Rondom de sportvelden van Spartaan 20 dienen niet meer bomen voor de uitbreiding van de sportvelden te worden gekapt dan strikt noodzakelijk. De boomkap ten behoeve van de aanleg van een haag is niet strikt noodzakelijk en deze bomen dienen dan ook te worden behouden.
16. Vóór de aanvang van kapwerkzaamheden dienen bomen met holten te worden gecontroleerd door een ter zake kundige1 op het gebied van vogels, op de aanwezigheid van vogels in de holtes buiten het broedseizoen. Door op de stam van de boom te kloppen dienen de vogels te worden verjaagd vóór de aanvang van de kapwerkzaamheden.
17. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing verleend wordt.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Het gaat om  aanvulling en verlenging van de op 21 augustus 2006 verleende ontheffing met kenmerk FF/75C/2004/0245B,

Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Herinrichting Zuiderpark” en betreft het Zuiderpark, gelegen in de deelgemeente Charlois in de gemeente Rotterdam]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL32">Noord-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[In het gebied vindt een samenhangend geheel van ruimtelijke ontwikkelingen plaats. Er zijn geen alternatieven aangedragen, de voorgenomen werkzaamheden zijn locatiegebonden en deels al in uitvoering na eerdere toekenning van ontheffing met kenmerk FF/75C/2004/0620.
De geplande werkzaamheden zijn niet bedreigend voor de gunstige staat van instandhouding van de in het plangebied voorkomende beschermde soorten. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen en aantasting fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezende uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
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			<otherType></otherType>
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			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
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			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht  en de  grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
6. De compenserende en mitigerende maatregelen zoals voorgesteld op pagina 12 van de Projectbeschrijving verlegging IJdoornlaan van Projectbureau Noordwaarts (2008) dienen te worden nageleefd.
7. Vóór de aanvang van kapwerkzaamheden dienen de bomen met holten te worden gecontroleerd door een ter zake kundige1 op de aanwezigheid van vogels in de holtes buiten het broedseizoen. Door op de stam van de boom te kloppen worden vogels verjaagd voor de aanvang van de kapwerkzaamheden.
8. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Het gaat om  aanvulling en verlenging van de op 21 augustus 2006 verleende ontheffing met kenmerk FF/75C/2004/0245B,

Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Verlegging IJdoornlaan" in de gemeente Amsterdam; IJdoornlaan ter hoogte van de Nieuwe Leeuwarderweg]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<species><![CDATA[Motacilla flava, Anthus pratensis, Limosa limosa, Vanellus vanellus, Perdix perdix, Haematopus ostralegus, Tringa totanus, Alauda arvensis]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Gezien de wateroverlast waardoor het Hoogheemraadschap van Delfland een aantal jaren achter elkaar is getroffen, heeft Delfland besloten tot een integrale aanpak om het gehele waterhuishoudkundig systeem beter te kunnen beheersen: het project ABC-Delfland (afvoer- en bergingscapaciteit). ABC-Delfland beoogt meer verwerkingsruimte te creëren voor een plotselinge toename van de waterhoeveelheid, zoals tijdens hevige regenbuien.
Bijvoorbeeld door water langer vast te houden, meer te bergen en overtollig water sneller af te voeren. Eén van deze maatregelen is de verdubbeling van de bergingscapaciteit van de Bergboezem polder Berkel, naar circa 1.200.000 m3. Als de hevige neerslag voorbij is en het peil in de boezem is gezakt, wordt de Bergboezem weer leeggepompt. Het project is locatiegebonden. Uit de ABC-studie ‘Water binnen veilige kade(r)s’ van juli 2000 is gebleken dat met name de Zwethzone (middelste en westelijke deel van de boezem) en langs de Schie en de Haagse Vliet (oostelijke deel van de boezem) het meest gevoelige deel van de boezem is, vanwege de smalle kanalen en de lange afstand die het water moet afleggen om de boezemgemalen te bereiken. Uit de ABC-studie is gebleken dat de bestaande bergingscapaciteit van de Bergboezem moet worden verdubbeld naar 1.200.000 m3. De Bergboezem Berkel is ter ontlasting van de Schie en de Haagse Vliet: het oostelijke deel van de boezem. Het effect van de Bergboezem is het grootst in de Schie, in het stedelijk gebied van Delft en ten zuiden van Delft. In de locatiekeuze van de Bergboezem als calamiteitenberging heeft meegespeeld de gunstige waterhoudkundige ligging dichtbij de boezem en de al bestaande waterbergingsfunctie tijdens een maalstop. Naar verwachting zal de calamiteitenberging eens in de 10 tot 25 jaar bij berging vanwege een maalstop en eens in de 25 tot 50 jaar bij de berging van boezemwater worden gebruikt. De periode van ingebruikname kan echter op voorhand niet worden voorspeld, waardoor het tevens mogelijk is dat deze in de kwetsbare perioden van de aanwezige beschermde soorten valt en exemplaren, eieren van vogels en/of vissen en pullen van vogels worden verstoord en/of gedood. Nadat de berging weer is leeggepompt, kunnen beschermde soorten het gebied weer betreden en zich weer voortplanten. Omdat de frequentie van ingebruikname van de berging gering is, de kans dat de berging in kwetsbare perioden van aanwezige beschermde soorten in gebruik wordt genomen tevens gering is en de berging maar voor een korte periode onder water staat, zal de gunstige staat van instandhouding van de lokale populaties van de aanwezige soorten niet in het geding komen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de broedvogels komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de inrichtingswerkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden te voorkomen.
12. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt verleend.
13. Bovenstaande maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Herinrichting van de Bergboezem polder Berkel" in de gemeenten Lansingerland en Pijnacker-Nootdorp; begrensd door de Ackerdijkse plassen en Polder Schieveen, de Polder Oude Leede en de Bovenvaart.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0181" userIdentity="Alterra1" derogation_reference="Alterra1-B-68-2010010315094377">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-01</licenseValidFrom>
		<licenseValidUntil>2013-08-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Aythya fuligula, Fulica atra, Anas clypeata, Gallinula chloropus, Anas querquedula]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Gezien de wateroverlast waardoor het Hoogheemraadschap van Delfland een aantal jaren achter elkaar is getroffen, heeft Delfland besloten tot een integrale aanpak om het gehele waterhuishoudkundig systeem beter te kunnen beheersen: het project ABC-Delfland (afvoer- en bergingscapaciteit). ABC-Delfland beoogt meer verwerkingsruimte te creëren voor een plotselinge toename van de waterhoeveelheid, zoals tijdens hevige regenbuien.
Bijvoorbeeld door water langer vast te houden, meer te bergen en overtollig water sneller af te voeren. Eén van deze maatregelen is de verdubbeling van de bergingscapaciteit van de Bergboezem polder Berkel, naar circa 1.200.000 m3. Als de hevige neerslag voorbij is en het peil in de boezem is gezakt, wordt de Bergboezem weer leeggepompt. Het project is locatiegebonden. Uit de ABC-studie ‘Water binnen veilige kade(r)s’ van juli 2000 is gebleken dat met name de Zwethzone (middelste en westelijke deel van de boezem) en langs de Schie en de Haagse Vliet (oostelijke deel van de boezem) het meest gevoelige deel van de boezem is, vanwege de smalle kanalen en de lange afstand die het water moet afleggen om de boezemgemalen te bereiken. Uit de ABC-studie is gebleken dat de bestaande bergingscapaciteit van de Bergboezem moet worden verdubbeld naar 1.200.000 m3. De Bergboezem Berkel is ter ontlasting van de Schie en de Haagse Vliet: het oostelijke deel van de boezem. Het effect van de Bergboezem is het grootst in de Schie, in het stedelijk gebied van Delft en ten zuiden van Delft. In de locatiekeuze van de Bergboezem als calamiteitenberging heeft meegespeeld de gunstige waterhoudkundige ligging dichtbij de boezem en de al bestaande waterbergingsfunctie tijdens een maalstop. Naar verwachting zal de calamiteitenberging eens in de 10 tot 25 jaar bij berging vanwege een maalstop en eens in de 25 tot 50 jaar bij de berging van boezemwater worden gebruikt. De periode van ingebruikname kan echter op voorhand niet worden voorspeld, waardoor het tevens mogelijk is dat deze in de kwetsbare perioden van de aanwezige beschermde soorten valt en exemplaren, eieren van vogels en/of vissen en pullen van vogels worden verstoord en/of gedood. Nadat de berging weer is leeggepompt, kunnen beschermde soorten het gebied weer betreden en zich weer voortplanten. Omdat de frequentie van ingebruikname van de berging gering is, de kans dat de berging in kwetsbare perioden van aanwezige beschermde soorten in gebruik wordt genomen tevens gering is en de berging maar voor een korte periode onder water staat, zal de gunstige staat van instandhouding van de lokale populaties van de aanwezige soorten niet in het geding komen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
			<activity code="30">Killing</activity>
		</activities>
		<methods>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de broedvogels komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de inrichtingswerkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden te voorkomen.
12. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt verleend.
13. Bovenstaande maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Herinrichting van de Bergboezem polder Berkel" in de gemeenten Lansingerland en Pijnacker-Nootdorp; begrensd door de Ackerdijkse plassen en Polder Schieveen, de Polder Oude Leede en de Bovenvaart.]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-08-18</licenseValidFrom>
		<licenseValidUntil>2013-05-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het gebied rondom Varsseveld-Sinderen biedt een beperkt aanbod aan verblijfsrecreatie.
De locatie aan de Harterinkdijk te Sinderen (het plangebied) is in het verleden in gebruik geweest als bungalowpark, echter de laatste jaren door omstandigheden in verval geraakt. De behoefte aan verblijfsmogelijkheden in het gebied zijn gebleven. Het streekplan Gelderland verwijst met betrekking tot dit gebied naar de Regionale Structuurvisie voor de Achterhoek. In deze visie is als ambitie opgenomen om recreatie en toerisme te profileren, waarbij recreatie en toerisme als belangrijke economische drager worden beschouwd.
De reden dat het bungalowpark juist op deze locatie opnieuw in gebruik wordt genomen is dat het naast de toeristische aantrekkelijke ligging, binnen het bestemmingsplan de juiste bestemming heeft. In de omgeving zijn op dit moment geen goede alternatieven voorhanden, waar op korte termijn een bungalowpark zal kunnen worden gestart.
Vanuit ervaring uit het verleden kan geconcludeerd worden dat, met de nodige zorgvuldigheid, een bungalowpark op de locatie samen kan gaan met de aanwezigheid van de das en steenuil. Ook in het verleden waren deze namelijk aanwezig. Er worden voldoende mitigerende en compenserende maatregelen getroffen waardoor de gunstige staat van instandhouding van de aanwezige beschermde soorten gewaarborgd blijft. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">aantasting leefgebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen dienen uitgevoerd te worden conform hoofdstuk 3, bijlage 1 en bijlage 2 uit het bij de aanvraag gevoegde rapport ‘Resort Sinderen, ontheffingsaanvraag steenuil en das’ van 23 april 2008.
9. Alle bovenstaande maatregelen dienen uitgevoerd te worden onder begeleiding van een ter zake kundige1 op het gebied van de soort waarvoor ontheffing wordt verleend.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Resort Sinderen BV" aan de Harterinkdijk 18 in de gemeente Oude IJsselstreek; begrensd door het Idinkbos, de Seesinkbeek en een boomkweekperceel]]></location>
		<licensedJustification></licensedJustification>
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	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0145" userIdentity="Alterra1" derogation_reference="Alterra1-B-78-2010020816001667">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2009-01-01</licenseValidFrom>
		<licenseValidUntil>2010-06-30</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Er zijn vier alternatieve locaties onderzocht op hun effecten en ecologisch rendement. Uiteindelijk heeft de afweging van verschillende factoren, waaronder kortste ecologische overbrugging over spoor en A2, minste fysieke beperkingen, minste verstoring en eigendomssituatie een duidelijke voorkeursvariant opgeleverd. De variant met de kortste overbrugging was ecologisch niet aantrekkelijk door de ligging van het militaire terrein in de directe aanloop tot het ecoduct. De variant met de minste fysieke beperkingen ging echter samen met de langste ecologische overbrugging en was bovendien net buiten het natuurgebied gelegen. De uitgewerkte voorkeursvariant levert een goed gemiddelde: een iets minder korte ecologische verbinding, relatief weinig fysieke beperkingen voor aanleg en in de directe aanloop (ook ten aanzien van het onderliggend wegennet) en een gunstige eigendomssituatie. Het ecoduct zal een positieve bijdrage leveren aan de instandhouding van de aangetroffen soorten doordat het leefgebied wordt uitgebreid. De verstoring, die optreedt als gevolg van de werkzaamheden, zal tijdelijk zijn. De werkzaamheden worden dusdanig vormgegeven, dat de verstoring die optreedt minimaal is. Daarnaast worden gedurende de uitvoerfase specifieke maatregelen getroffen om aantasting van de in het gebied aanwezige natuurwaarden te minimaliseren. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezende uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht  en de  grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Alle compenserende en mitigerende voorwaarden zoals genoemd in hoofdstuk 4 van het bij de aanvraag gevoegde rapport ‘Ecoduct Weertbergen. Onderzoek in het kader van Flora- en faunawet en Natuurbeschermingswet’ van oktober 2007 dienen te worden uitgevoerd met in achtneming van onderstaande voorwaarden.
10. Voorafgaand aan de kap dient te worden gecontroleerd of holtes door de grote bonte specht in gebruik zijn. Als dit zo is, dienen de betreffende bomen te worden ontzien totdat is vastgesteld dat de holtes niet meer in gebruik zijn.
11. Alle bovenstaande mitigerende maatregelen dienen te worden uitgevoerd door en/of onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Aanleg Ecoduct Weerterbergen" in de gemeenten Weert en Nederweert]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0257" userIdentity="Alterra1" derogation_reference="Alterra1-B-79-2010020817295677">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-01</licenseValidFrom>
		<licenseValidUntil>2009-03-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Accipiter gentilis]]></species>
		<regions>
			<region code="NL32">Noord-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Er is door u geen alternatief geboden. Het project is locatiegebonden. In uw bestemmingsplan Landelijk gebied zijn de gronden van de voormalige vuilstort bestemd voor Natuur- en landschapsdoeleinden. Voor dit veenweidegebied wordt de landschappelijke openheid erg belangrijk gevonden en het gebruik als grasland. De voormalige vuilstort langs de Amsteldijk-Zuid heeft een beplanting met onder andere populier. Het omliggende veenweidegebied is onderdeel van natuurgebied Uithoorn en is in erfpacht uitgegeven aan landschap Noord-Holland. In het beheerplan is de doelstelling van dit gebied beschreven als behoud en ontwikkeling van een open halfnatuurlijk landschap. Het hoge, dichtbegroeide populierenbos past niet in deze doelstelling en heeft bovendien een negatief effect op weidevogels in de omgeving van het plangebied. De natuurwaarde van een hoog en gesloten populierenbos is klein. Met het rooien van de populieren verdwijnen ook nesten van buizerd en havik. In de omgeving zijn echter andere geschikte locaties aanwezig voor buizerd en havik om tot broeden te komen. De door u gekozen werkwijze is bevredigend. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen, aantasting fourageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd  en de havik komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Gedurende de werkzaamheden dient rekening gehouden te worden met het broedseizoen van de buizerd en de havik. Verstoring van broedgevallen dient te worden voorkomen. Werkzaamheden dienen buiten de broedperiode van aanwezige soorten uitgevoerd te worden. Ik wijs u erop dat voor het broedseizoen geen standaardperiode wordt gehanteerd in het kader van de Flora- en faunawet. Van belang is of een broedgeval verstoord wordt, ongeacht de periode. Het einde van het broedseizoen dient te worden vastgesteld door een ter zake kundige1 op het gebied van vogels.
8. Vóór aanvang van de kapwerkzaamheden dienen, door een ter zake kundige1 op het gebied van vogels, bomen met een nest- of verblijfplaats van de buizerd en de havik te worden gecontroleerd op de aanwezigheid van vogels. Indien aanwezigheid is uitgesloten, kunnen kapwerkzaamheden uitgevoerd worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Omvormen beplanting vuilstort Amsteldijk-Zuid" gelegen aan de Amsteldijk-Zuid in de gemeente Uithoorn]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0054" userIdentity="Alterra1" derogation_reference="Alterra1-B-80-2010021610563079">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-24</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De ontwikkeling van de planlocatie is onderdeel van een groter geheel en sluit aan op reeds in ontwikkeling zijnde plannen op aangrenzende terreinen. De bestemming voor de planlocatie is reeds vastgelegd in het gemeentelijke bestemmingsplan, wat de ontwikkeling van het terrein mogelijk maakt. Gezien de ontwikkeling van de omgeving is het niet mogelijk de voorgenomen werkzaamheden op een andere locatie uit te voeren. De inrichting en werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding van de in het plangebied aanwezige beschermde soorten blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Tijdens het broedseizoen van de grote bonte specht mogen geen verstorende werkzaamheden ten aanzien van deze soort worden uitgevoerd. Het broedseizoen van de grote bonte specht loopt globaal van april tot en met juli. Afhankelijk van het seizoen en de weersomstandigheden kan deze periode langer dan wel korter zijn. De geschiktheid van de periode voor het uitvoeren van de werkzaamheden dient te worden bepaald door een ter zake kundige1 op het gebied van vogels.
8. Direct voorafgaand aan de kap dienen de eventueel aanwezige spechten te worden verjaagd uit de bomen met geschikte holten, mits is vastgesteld dat eventueel aanwezige jongen de nesten niet meer nodig hebben. Het verjagen kan worden gedaan door de bomen zacht te schudden met behulp van de grijpers van de kraan. Als dit niet tot de mogelijkheden behoort, kunnen de bomen ook beklopt worden met een rubber hamer.
9. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van vogels.
10. Bovenstaande mitigerende maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. De werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Nieuw-Rhijngeest te Oegstgeest" in de gemeente Oegstgeest ten noorden van de kruising tussen de Ir. A. Tjalmaweg (N206) en de A44]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0107a" userIdentity="Alterra1" derogation_reference="Alterra1-B-81-2010021611055728">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-26</licenseValidFrom>
		<licenseValidUntil>2011-06-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Strix aluco]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De Rijksweg N34 gaat momenteel door Ommen heen. Dit levert allerlei problemen op. De nieuwe autoweg (doortrekken van de N36) biedt een oplossing voor de verkeersproblemen op de bestaande N34. Het verkeer richting centrum Ommen kan niet goed doorrijden.
Vooral in de spits ontstaan hierdoor files en onveilige verkeerssituaties. Omwonenden hebben last van het geluid en stank van het verkeer. Daarnaast verbetert het hoofdwegennet tussen Twente en Noord-Nederland en de regionale verbinding tussen Hardenberg en Zwolle. In de MER die in 2000 is verschenen is een groot aantal tracés onderzocht, waarbij ook de milieuaspecten van de verschillende oplossingen in beeld zijn gebracht.
Hierbij is rekening gehouden met eisen vanuit verkeersveiligheid, het leveren van een verantwoorde inpassing in het landschapspatroon en met de beleving van het landschap door de bewoners en weggebruikers. Het voorliggende tracé is gekozen als beste optie door de Minister van Verkeer en Waterstaat in samenspraak met de Minister van Volkshuisvesting, Ruimtelijke Ordening en Milieubeheer. De voorgestelde mitigerende en compenserende maatregelen voor dit tracé leiden ertoe dat de gunstige staat van instandhouding voor de verschillende beschermde soorten niet in het geding komt. Het project biedt een bevredigende oplossing. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">Schuur slopen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de bosuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
13. De sloop van het schuurtje dient pas uitgevoerd te worden wanneer duidelijk is dat de bosuil niet aanwezig is. Dit moet door een ter zake kundige1 op het gebied van uilen bekeken worden.
14. In overleg met een ter zake kundige1 op het gebied van uilen dienen in de omgeving van het schuurtje voor de bosuil twee kasten opgehangen te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Omleiding Ommen N34/N36". Het gedeelte van het tracé betreffende de Omleiding is gelegen tussen de N48 en de Witte Paal (Rijksweg 36)]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0241" userIdentity="Alterra1" derogation_reference="Alterra1-B-82-2010021616381962">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-22</licenseValidFrom>
		<licenseValidUntil>2013-08-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het plangebied is in eigendom van de firma Norel. De compensatiemaatregelen van het project zijn onderdeel van een integraal plan van de gemeente Apeldoorn, waarbij naast industriële ontwikkeling, ook natuurdoelen een belangrijk uitgangspunt voor de planontwikkeling zijn. Bij de integrale planafweging is gekeken naar diverse alternatieve locaties.
Het bosgebied met een daarin gelegen restant van een sprengkop van de Eendrachtsspreng dat gelegen is ten westen van de beoogde uitbreidingslocatie is afgevallen voor industriële uitbreiding Zuidwestpoort, vanwege het voorkomen van diverse beschermde diersoorten waaronder ringslang, kleine hagedis en ijsvogel. Daarnaast is voor de uitbreiding van de industriële bebouwing Norellocatie ook gedacht aan een alternatieve locatie aan de oostkant die nu in gebruik is voor opslag van industrieel materiaal en al een industriële bestemming heeft. Op advies van de ecologen van de gemeente Apeldoorn krijgt deze locatie, de zogenaamde ringslangontwikkellocatie, een natuurbestemming. Deze locatie grenst rechtstreeks aan een inmiddels drooggevallen tak van de Eendrachtsspreng.
Dit te herstellen/beschermen beoogde natuurgebied vormt dan een goed beschermd onderdeel van de groene mal (hoofdraamwerk groenstructuur stedelijk gebied Apeldoorn) aan de zuidkant van Apeldoorn. Het project is daarom locatiegebonden. Indien de compensatiemaatregelen plaatsvinden zoals beoogd, is er op lange termijn geen sprake van achteruitgang van het leefgebied van de grote bonte specht. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
Voorafgaand aan de kap van de nestbomen van de grote bonte specht dient een ter zake kundige1 op het gebied van vogels te bepalen of het nest vrij is en er geen broedende grote bonte spechten of jongen meer aanwezig zijn. Indien de grote bonte specht aanwezig is, dient gewacht te worden met de kapwerkzaamheden totdat de jongen zijn uitgevlogen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Ontwikkeling terrein Norel" in de gemeente Apeldoorn tussen bedrijventerrein Ugchelen, het Wegenerterrein en de Eendrachtspreng]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0258" userIdentity="Alterra1" derogation_reference="Alterra1-B-83-2010021617095867">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-19</licenseValidFrom>
		<licenseValidUntil>2013-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major, Dendrocopos Minor, Dryocopus martius]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Van de heidegebieden ten zuiden van Nijmegen is nog maar weinig over. Deze gebieden zijn bijna geheel begroeid met bos. Hierin zijn Mookerschans, Heumense Schans en Mulderskop als klein heiderestant bewaard gebleven. Om de achteruitgang van bijzondere heidefauna te stoppen en het voortbestaan van deze soorten op lange termijn te garanderen, dienen verbindingen tussen de heideterreinen gerealiseerd te worden. Nederland heeft een internationale verantwoordelijkheid voor karakteristieke heidesoorten. Veel van deze soorten staan op de Rode Lijst of staan vermeld op de bijlagen bij de Europese Habitatrichtlijn.
De vergroting van het heideareaal rond de huidige kerngebieden is nodig om de bijzondere soorten een kans te bieden de populaties uit te breiden. Dit is nodig, omdat het bij veel soorten om kleine, kwetsbare en zeer geïsoleerde populaties gaat. Het verbinden van de kerngebieden biedt de heidefauna de mogelijkheid nieuwe of in het verleden bezette gebieden opnieuw te koloniseren. Er is geen andere locatie voorhanden om de leefomstandigheden van de beschermde reptielen ter plekke te verbeteren. Bos dient gekapt en gedund te worden ten behoeve van de beschermde reptielen. Door het uitvoeren van het project zal de gunstige staat van instandhouding van de aanwezige reptielenpopulaties sterk verbeteren. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
			<activity code="82">Deliberate disturbance during the period of rearing</activity>
		</activities>
		<methods>
			<method code="FT">verstoring foerageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht, kleine bonte specht en de zwarte specht komt niet in gevaar,]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het kappen van dichte bosopstanden waar geen reptielen verwacht worden, dient plaats te vinden buiten het broedseizoen van vogels.
9. Locaties waar vaste rust- en verblijfplaatsen verwacht worden dienen zoveel mogelijk ontzien te worden tijdens de werkzaamheden. Zwaar materieel dient over van te voren vastgestelde werkpaden te rijden.
15. De nestbomen van de spechten dienen niet gekapt te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)
Het deelgebied “Mulderskop” ligt ingesloten tussen de buiten gebruik zijnde goederenspoorlijn Nijmegen-Groesbeek en de spoorlijn Nijmegen-Boxmeer, het deelgebied "Heumensoord" ligt aan de westzijde van de spoorlijn Nijmegen Boxmeer, het deelgebied "Spoorlijn" omvat de spoorlijn vanaf Heumensoord tot Mulderskop, deelgebied "’t Gruske" bestaat uit 5 bospercelen ten oosten van het deelgebied "Spoorlijn" en deelgebied "Mookerschans" is gelegen ten noorden van Mook.]]></comments>
		<location><![CDATA[het project "Heideherstel Nijmegen Mook" in de gemeenten Nijmegen, Mook en Middelaar. Zie commentaar voor een verdere afbakening van het gebied.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0389" userIdentity="Alterra1" derogation_reference="Alterra1-B-84-2010021617415948">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-01</licenseValidFrom>
		<licenseValidUntil>2009-06-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Op de Nijmeegse woningmarkt is een groot tekort aan woningen ontstaan. Het project ‘Dorpensingel-West fase 2 (werknaam)’ maakt deel uit van een groter project voor de aanleg van 12.500 woningen in VINEX-wijken. Het project ‘Dorpensingel-West fase 2 (werknaam)’ is van belang voor het woon-werkverkeer van en naar Woonpark Oosterhout en als af- en aanvoerroute voor werkverkeer tijdens de aanleg van de woningen in Groot Oosterhout.
Indien het project ‘Dorpensingel-West fase 2 (werknaam)’ niet wordt uitgevoerd, blijven onveilige verkeerssituaties bestaan, en loopt de nieuwbouw van de wijk Groot Oosterhout vertraging op door vervoersproblemen. In verband met de sanering van de zoutloods die noodzakelijk is vanwege verontreiniging met cyanide en chloride, is behoud van de zoutloods, en daarmee behoud van het nest van de kerkuil, niet mogelijk. De mitigerende maatregelen die bij het project worden getroffen, zorgen ervoor dat de gunstige staat van instandhouding van de beschermde soorten niet in het geding komt. Er wordt zorgvuldig gehandeld. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen met nestplaats</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de kerkuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
8. Ter compensatie van de sloop van de zoutloods dienen vóór de sloop tenminste twee nestkasten te worden geplaatst op geschikte locaties in de nabije omgeving. Een ter zake kundige1 op het gebied van de kerkuil dient te bepalen welke locaties geschikt zijn.
9. De sloop van de zoutloods dient plaats te vinden buiten het broedseizoen van de kerkuil (dat vrijwel het gehele jaar kan omvatten). Enkele dagen voorafgaand aan de sloop dient het nest te worden geinspecteerd. Indien er zich nog jongen in het nest bevinden, dient met de sloop gewacht te worden totdat deze uit zichzelf de nestplaats verlaten hebben.
14. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.
15. Bij de toekomstige ontheffingsaanvraag voor Groot Oosterhout dienen de dan optredende cumulatieve effecten op het leefgebied van de kerkuil en de poelkikker te worden meegenomen, waarbij opnieuw mitigerende en/of compenserende maatregelen aan de orde te komen. Hiervoor dienen de mogelijkheden in 2009 te worden onderzocht.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Dorpensingel-West fase 2 (werknaam)", in de gemeente Nijmegen. Het betreft het tracé vanaf de rotonde Sportpark Oost aan de Stadsas tot de rotonde Groot Oosterhout.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0397" userIdentity="Alterra1" derogation_reference="Alterra1-B-85-2010021717445311">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-01</licenseValidFrom>
		<licenseValidUntil>2010-03-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Bij de ruimtelijke ontwikkeling van het terrein is geen alternatieve aanpak ten aanzien van het bosperceel mogelijk. Er kan mogelijk in beperkte mate bos gepaard worden bij de herinrichting van het terrein, maar de kans dat gespaarde bomen de geplande verhoging van het maaiveldpeil, danwel verlaging van het waterpeil overleven is gering. In de nieuwe situatie wordt wel voorzien in een groenstrook zodat in de toekomst weer geschikt habitat wordt gecreëerd. In de directe omgeving zijn nog enkele groenzones en bospercelen beschikbaar als uitwijkmogelijkheid. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>5</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De bomen met spechtenholten dienen zo mogelijk te worden gespaard en opgenomen in toekomstige houtopstanden. Indien ze moeten worden verwijderd dient de kap ná het broedseizoen plaats te vinden.
8. Vóór de aanvang van de kapwerkzaamheden buiten het broedseizoen dienen spechtenholten gecontroleerd te worden op de aanwezigheid van vogels. Bij het aantreffen van een grote bonte specht in een holte dient door een ter zake kundige1 op het gebied van vogels beoordeeld te worden of er al dan niet sprake is van een broedgeval. Eventueel aanwezige vogels dienen hierbij verjaagd te worden door met een hamer op de stam te kloppen.
9. Voor de grote bonte specht geschikte boomtypen dienen te worden gespaard en op geschikte plaatsen bijgeplant te worden. In grote te handhaven bomen dienen broedkasten voor deze spechten te worden aangebracht. Locaties en wijze van ophangen dienen te worden bepaald door een ter zake kundige1 op het gebied van vogels.
10. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van vogels.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[Project "Bouwlocatie Verkadeterrein Zaandam" in de gemeente Zaandam. een voormalig sportterrein in de bebouwde kom van Zaandam, aan de westzijde begrensd door de N203]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0426" userIdentity="Alterra1" derogation_reference="Alterra1-B-86-2010021809113922">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-01</licenseValidFrom>
		<licenseValidUntil>2011-10-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Er zijn geen alternatieven gegeven. Het gaat om een restant van een vervallen schuur. Wanneer er weer een grote storm komt wordt gevreesd dat deze in elkaar zal storten, hetgeen ook niet veilig is voor de steenuil. Daarom dient de schuur gesloopt te worden voordat de uilen weer gaan broeden. Een alternatief is dan ook niet aan de orde.
Ecologisch gezien zal de sloop van de schuur voor de steenuil niet betekenen dat er geen broedlocaties overblijven. De steenuil heeft voorheen altijd gebruik gemaakt van een andere, nabijgelegen locatie en zal daar ook naar terug kunnen keren. Er is daarom geen alternatief noodzakelijk, zeker omdat de schuur in verval is en misschien al snel geen nestlocatie meer kan bieden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen schuur</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De schuur dient gesloopt te worden in de periode september-november.
8. Een ter zake kundige1 op het gebied van de steenuil dient te controleren of de steenuil nog aanwezig is. Op het moment dat de steenuil niet aanwezig is in de schuur dient deze zo snel mogelijk gesloopt te worden. Wanneer de steenuil nog wel aanwezig is, dient gewacht te worden met slopen tot de steenuil niet meer in de schuur aanwezig is.
9. Bij de nieuwe schuur dient, in overleg met een ter zake kundige1 op het gebied van steenuilen een steenuilenkast opgehangen te worden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Sloop restant kippenschuur" in de gemeente Wageningen]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0222" userIdentity="Alterra1" derogation_reference="Alterra1-B-87-2010021809202227">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-02</licenseValidFrom>
		<licenseValidUntil>2013-08-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis, Dendrocopos major]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Mogelijke alternatieven voor het project zijn in ruime mate onderzocht in achtereenvolgens Plan-MER, Structuurplan en Project-MER. De voorgenomen activiteiten zijn in het kader van het Structuurplan beoordeeld in een strategische milieubeoordeling (of plan- MER procedure). De activiteiten zijn op een ander abstractieniveau in het licht van een milieu-effectenstudie (project-MER) beoordeeld. Dit gebiedsprogramma beoogt een kwaliteitsverbetering voor natuur, landschap en recreatie, alsmede invulling geven aan de reconstructiedoelen, waaronder herstel landschappelijke kwaliteit, nieuwe natuur, vermindering milieubelasting van de kernen, het initiëren van nieuwe economische dragers en behoud van de leefbaarheid van het platteland. De gunstige staat van instandhouding komt niet in gevaar, omdat in de directe omgeving in ruime mate geschikt leefgebied aanwezig blijft voor de beschermde soorten. Het is aannemelijk gemaakt dat de natuurwaarden in eerste instantie moeten worden aangetast om het voorgenomen project te kunnen verwezenlijken. De werkwijze is zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen. De werkzaamheden zijn van tijdelijke aard. Uiteindelijk zullen er vergelijkbaar leefgebied op land ontstaan en een verbeterd watersysteem. Het project is probleemoplossend. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen, aantasting leefgebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezende uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht  en de  grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen genoemd in hoofdstuk 5 van het bij de aanvraag gevoegde rapport “Uitbreiding Bakelse Plassen, projectomschrijving i.k.v. Flora- en Faunawet” van maart 2008 en in de brief van 30 juli 2008 dienen te worden uitgevoerd met in achtneming van onderstaande voorwaarden.
8. Vóórafgaand aan het kappen van bomen dient een ter zake kundige1 op het gebied van vogels te controleren of de holten waar de groene specht en de grote bonte specht gebruik van kunnen maken in gebruik zijn. Indien holten in gebruik zijn dienen de betreffende bomen te worden ontzien totdat is vastgesteld dat de holten niet meer in gebruik zijn.
16. Bovengenoemde maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Integraal Gebiedsprogramma Bakelse plassen" gelegen in de gemeente Gemert-Bakel direct ten noorden van de dorpen Bakel en Milheeze.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0409" userIdentity="Alterra1" derogation_reference="Alterra1-B-88-2010021809352075">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-07</licenseValidFrom>
		<licenseValidUntil>2011-02-28</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Het project voorziet in achterstallig onderhoud. De werkzaamheden zijn daarmee locatiegebonden. De bomenkap in de woonwijk Plaswijck is nodig vanwege de veiligheid van wandelaars en in een enkel geval om groentechnische redenen.
De bomen zijn op geringe onderlinge afstand geplant en daardoor te lang en te dun uitgegroeid, waardoor in de huidige situatie veel taksterfte optreedt in de onderste boomlaag.
In het Noorderhout worden ook bomen verwijderd omdat deze veel schaduw werpen, wat een negatieve invloed heeft op de aanwezige ringslangpopulatie. De grondafdekking in het Noorderhout is noodzakelijk vanuit milieutechnisch oogpunt vanwege de onder het park aanwezige afvalstort. Hierbij is een alternatieve locatie niet aan de orde. De werkwijze is zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding gewaarborgd blijft. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
10. De bomen met spechtenholten dienen, waar mogelijk, te worden gespaard. Indien ze daarentegen onherroepelijk moeten worden verwijderd, dient het kappen buiten het broedseizoen plaats te vinden.
11. Vóór aanvang van de kapwerkzaamheden dienen spechtenholten gecontroleerd te worden op de aanwezigheid van spechten. Eventueel aanwezige vogels dienen hierbij verjaagd te worden, bijvoorbeeld door met een hamer op de stam te kloppen.
12. Wanneer bomen met holten gekapt worden, dienen ter compensatie enkele nestkasten opgehangen te worden in de directe omgeving en in geschikte te handhaven bomen. Deze nestkasten dienen vóór de kap opgehangen te worden.
13. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soorten waarvoor ontheffing wordt verleend.
14. Bovenstaande mitigerende maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[Project "Achterstallig onderhoud Groenvoorziening Noorderhout/Plaswijck" gelegen in de woonwijk Plaswijck tussen de rijksweg A12 en de Reeuwijkse Plassen en de groenstrook Noorderhoutin het noordelijk deel van de bebouwde kom van Gouda]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0402B" userIdentity="Alterra1" derogation_reference="Alterra1-B-89-2010021809495382">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-14</licenseValidFrom>
		<licenseValidUntil>2011-07-15</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major, Tyto alba]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Van de heidegebieden ten zuiden van Nijmegen is nog maar weinig over. Deze gebieden zijn bijna geheel begroeid met bos. Hierin zijn Mookerschans, Heumense Schans en Mulderskop als klein heiderestant bewaard gebleven. Om de achteruitgang van bijzondere heidefauna te stoppen en het voortbestaan van deze soorten op lange termijn te garanderen, dienen verbindingen tussen de heideterreinen gerealiseerd te worden. Nederland heeft een internationale verantwoordelijkheid voor karakteristieke heidesoorten. Veel van deze soorten staan op de Rode Lijst of staan vermeld op de bijlagen bij de Europese Habitatrichtlijn.
De vergroting van het heideareaal rond de huidige kerngebieden is nodig om de bijzondere soorten een kans te bieden de populaties uit te breiden. Dit is nodig, omdat het bij veel soorten om kleine, kwetsbare en zeer geïsoleerde populaties gaat. Het verbinden van de kerngebieden biedt de heidefauna de mogelijkheid nieuwe of in het verleden bezette gebieden opnieuw te koloniseren. Er is geen andere locatie voorhanden om de leefomstandigheden van de beschermde reptielen ter plekke te verbeteren. Bos dient gekapt en gedund te worden ten behoeve van de beschermde reptielen. Door het uitvoeren van het project zal de gunstige staat van instandhouding van de aanwezige reptielenpopulaties sterk verbeteren. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
			<activity code="82">Deliberate disturbance during the period of rearing</activity>
		</activities>
		<methods>
			<method code="FT">slopen gebouw, aantasting foerageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen dwingende redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht en de Kerkuil komt niet in gevaar,]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[17. Voorafgaand aan de kapwerkzaamheden dient door een ter zake kundige1 gekeken te worden of de aanwezige holten in bomen niet in gebruik zijn als nestlocatie door de grote bonte specht. Indien er een broedgeval wordt aangetroffen dan dient met de kap van de betreffende boom gewacht te worden tot de jongen vliegensvlug en uitgevlogen zijn.
18. Bij het slopen van het gebouw waarin de kerkuil verblijft, zal veldbegeleiding aanwezig zijn, waarbij gekeken wordt naar maatwerk. Daarnaast dient bij de inrichting en het beheer van de omgeving van de nestlocaties rekening gehouden te worden met de voedseldieren van deze uilen.
19. Er dient jaarlijks een voortgangsrapportage ingediend te worden bij Dienst Regelingen. Hierin moet beschreven worden welke werkzaamheden wanneer uitgevoerd zijn, welke soorten hierbij tegengekomen zijn en hoe hiermee omgegaan is.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Het betreft een aanpassing van de op 27 mei 2008 verleende ontheffing FF/75C/2007/0402A.
1 Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Realisatie wijk Schuytgraaf" in de gemeente Arnhem.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0311" userIdentity="Alterra1" derogation_reference="Alterra1-B-90-2010021810014584">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-09-16</licenseValidFrom>
		<licenseValidUntil>2013-08-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het Westerhonk is het hoofdterrein voor mensen met een ernstige verstandelijke beperking.
De voorgenomen herinrichting betreft een bestaand terrein van een zorginstelling voor verstandelijk gehandicapten. Conform overheidsbeleid is het wenselijk de cliënten zoveel mogelijk te integreren in de maatschappij. De voorgestelde herinrichting voorziet in deze intergratie aangezien particulieren ook op het terrein gaan wonen. Ook wordt voor de cliënten verbeterde huisvesting gerealiseerd met meer privacy en woonoppervlak.
De bestaande huisvesting voldoet volgens u en volgens het Ministerie van Volksgezondheid, Welzijn en Sport niet meer aan de eisen die worden gesteld voor huisvesting in de gehandicaptenzorg. Er is geen locatie alternatief aangeboden aangezien het een herinrichting van een bestaand complex betreft en het in die zin dus locatiegebonden is. Het plangebied heeft een groen karakter met uitgebreide gazons en bosschages. Door de geringe ouderdom en het intensieve beheer zijn de natuurpotenties niet optimaal ontwikkeld.
Het is de verwachting dat er na de herinrichting en middels het handhaven van bos zeker geen verslechtering optreedt van de natuurwaarde. Tevens maakt de herontwikkeling een nieuw structureel beheer van het terrein mogelijk. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="11">In the interests of public health</reason>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
Voorafgaand aan de kap van de nestbomen van de grote bonte specht dient een ter zake kundige1 op het gebied van vogels te bepalen of het nest vrij is en er geen broedende grote bonte spechten of jongen meer aanwezig zijn. Indien de grote bonte specht aanwezig is, dient gewacht te worden met de kapwerkzaamheden totdat de jongen zijn uitgevlogen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vli]]></comments>
		<location><![CDATA[het project "Herinrichting Woongebied Polanen" in de gemeente Westland]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0321" userIdentity="Alterra1" derogation_reference="Alterra1-B-91-2010021810092168">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-17</licenseValidFrom>
		<licenseValidUntil>2009-03-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[De te slopen boerderij en stal staan sinds enige tijd leeg en zijn inmiddels sterk in verval geraakt. De verwachting is dat de bebouwing niet duurzaam als nestlocatie zal blijven fungeren. De drie alternatieve leefgebieden zijn geselecteerd om de volgende redenen:
- Ligging in nabijheid van het plangebied en bestaande foerageergebieden.
- Geen ander broedgeval van de steenuil binnen een straal van 300 meter.
- Aanwezigheid van boerderijen/bomen (om de nestkasten op te hangen).
- Aanwezigheid van geschikte leefomgeving en voldoende rust.
Het bestaande bedrijventerrein ligt aan de zuidzijde van Lemelerveld en is ingeklemd door het Overijsselsch Kanaal aan de westzijde, de bebouwde kom van Lemelerveld aan de noordzijde en de Provinciale weg N-348 aan de oostzijde van het plangebied. Uitbreiding van het bedrijventerrein in westelijke, noordelijke en oostelijke richting is dus niet mogelijk. Het project is daarmee plaatsgebonden.
De inrichting en werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen schuur</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De maatregelen genoemd onder de punten J. en K. van de bij de aanvraag gevoegde projectomschrijving ‘Steenuil – bedrijventerrein Lemelerveld’ van 26 juni 2008 dienen te worden uitgevoerd met inachtneming van de onderstaande voorwaarden.
8. Het verwijderen van de huidige verblijfplaats van de steenuil dient uitgevoerd te worden in de periode oktober tot eind februari. In verband met het aanpassingsvermogen van de steenuil, dient dit zo vroeg mogelijk in deze periode plaats te vinden.
9. Vóórdat tot de sloop van de bebouwing wordt overgegaan, dient door een ter zake kundige1 te worden vastgesteld dat in het te slopen gebouw op dat moment geen nesten met eieren of nestgebonden jongen aanwezig zijn of dat de uilen (en andere gebouwbewonende vogels) broedgedrag vertonen. Bij een dergelijke constatering dient de sloop uitgesteld te worden totdat de (jonge) steenuilen (en eventuele andere vogels) het nest verlaten hebben.
10. Indien uit dit onderzoek blijkt dat er geen bewoond nest aanwezig is, dient de boerderij te worden gestript. Een eventueel aanwezige steenuil krijgt daardoor de mogelijkheid om uit te wijken.
11. Alle bovenstaande mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soort waarvoor ontheffing wordt aangevraagd.
12. De drie opgehangen kasten dienen duurzaam beheerd en onderhouden te worden door IVN Raalte.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project  "Steenuil-Bedrijventerrein Lemelerveld", in de gemeente Dalfsen. Het betreft het gebied aan de Parallelweg 18, 8152 BE te Lemerveld]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0346" userIdentity="Alterra1" derogation_reference="Alterra1-B-92-2010021810165747">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-16</licenseValidFrom>
		<licenseValidUntil>2009-10-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[In 2004 heeft het Ministerie van VROM met de stadsregio, de provincie en de gemeente Arnhem, Nijmegen en Overbetuwe het "Convenant Woningbouwafspraken 2005-2009" gesloten. Daarin staat dat er in de periode tot en met 2009 bijna 25.000 woningen moeten worden opgeleverd. Voor de periode 2010-2015 geldt vooralsnog een opgave van circa 15.500 woningen. Voor deze forse bouwopgave zijn met de gemeenten in de stadsregio afspraken gemaakt in de vorm van woonconcessies per gemeente, op basis waarvan het de gemeente vrij staat woningen te bouwen binnen de contour woningbouw. De contour woningbouw is vastgelegd in het Regionaal Plan 2005-2020 van Stadsregio Arnhem-Nijmegen. Het Regionaal Plan is een uitwerking van het Streekplan Gelderland 2005. Binnen de contour woningbouw bepalen de gemeenten zélf hoeveel woningen er gebouwd worden. De contouren liggen meestal om bestaande bebouwingsgrenzen. De gemeente Westervoort heeft met de stadsregio afspraken gemaakt dat Westervoort 461 woningen zal bouwen tot 2010. Dit om te kunnen voldoen aan de afspraken met het Ministerie van VROM. Voor de periode daarna zullen opnieuw afspraken moeten worden gemaakt. Het plangebied De Schans ligt voor wat betreft de woningbouw binnen de contour woningbouw.
In de afspraken met de stadsregio zijn voor dit plangebied maximaal 76 woningen opgenomen, zoals ook in de Structuurschets voor De Schans is aangegeven. Het doel van het project is om onder meer de aanwezige archeologische, landschappelijke en cultuurhistorische waarden in het gebied weer zichtbaar en beleefbaar te maken. Op basis van het Belvedèrebeleid (behoud door ontwikkeling) is een inrichtingsvoorstel gemaakt waarbij de fortificatie van het centrumbastion weer zichtbaar wordt gemaakt in het landschap en de oude stallen van de Heegsche Buwing worden vervangen door woningen. Om dit doel te bereiken is een financiële drager nodig. Dit bestaat uit de bouw van de 76 woningen.
Het project is hiermee plaatsgebonden. Het zuidelijke deel van het plangebied is niet beschikbaar als alternatieve locatie. Dit deel van het plangebied is een Rijksmonument vanwege de archeologische waarde van het gebied. In dit deel van het plangebied mag daarom niet worden gebouwd. Inrichting en/of werkwijze zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen schuren en gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De maatregelen genoemd in §1.4 van de bij de aanvraag gevoegde "Projectomschrijving ontheffingsaanvragen Flora- en faunawet De Schans te Westervoort" van 8 juli 2008 dienen te worden uitgevoerd met inachtneming van onderstaande voorwaarden.
8. Bij gefaseerd kappen van de bomenrij is het niet nodig om de werkzaamheden binnen de overwinteringsperiode uit te voeren. De nieuwe laan dient al wel gedeeltelijk te worden aangeplant vóórdat de resterende populieren worden gekapt.
10. Ten zuiden van het plangebied dienen onder begeleiding van een ter zake kundige1 minimaal drie kasten opgehangen te worden en dient daar het foerageergebied rond de nieuwe steenuilkast waar nodig versterkt te worden.
11. De steenuilenkasten dienen vóór de sloop van de vaste rust- en verblijfplaats in het gebied te zijn opgehangen en ook de maatregelen ter versterking van het foerageergebied, zoals beschreven op de pagina’s 9 en 10 van de bij de aanvraag gevoegde "Projectomschrijving ontheffingsaanvragen Flora- en faunawet De Schans te Westervoort" van 8 juli 2008 dienen vóór de sloop uitgevoerd te zijn.
12. Bij de woning Schans 7 dient een steenuilkast geplaatst te worden.
13. Het slopen van de woning met een vaste rust- en verblijfplaats van de steenuil dient in de periode 1 oktober tot eind februari plaats te vinden. De andere gebouwen kunnen buiten deze periode gesloopt worden.
14. Alle bovenstaande werkzaamheden dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de soort waarvoor ontheffing is verleend.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het gebied van bijna 13 hectare ten zuiden van Westervoort, ten oosten van De Schans/Loodijk]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0373" userIdentity="Alterra1" derogation_reference="Alterra1-B-93-2010021810321729">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-17</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba, Athene noctua]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[U heeft in de door u op 3 februari 2006 ingediende ontheffingsaanvraag met kenmerk FF/75C/2006/0025 al aannemelijk gemaakt dat alternatieve locaties en werkwijzen ongeschikt zijn. De destijds gemaakte beoordeling van 31 oktober 2006 acht ik nog steeds valide. Er is derhalve voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">aantasting forageergebied</method>
		</methods>
		<reasons>
			<reason code="12">In the interests of public safety</reason>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>3</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>0</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de kerkuil en de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Dit is een aanvulling op het project waarvoor op 31 oktober 2006 ontheffing is verleend met kenmerk FF/75C/2006/0025.

Specifieke voorwaarden
14. Indien met betrekking tot de kerkuil en de steenuil zich broedgevallen voordoen in het plangebied, dient een rustzone rondom het broedgeval aangehouden te worden om te voorkomen dat nesten worden verstoord of vernietigd. Binnen de rustzone mogen geen werkzaamheden worden uitgevoerd.
Voor broedvogels van open vlaktes (weide- en akkervogels) en roofvogels geldt een rustzone van minimaal 50 meter, voor andere vogels geldt een rustzone van minimaal 20 meter.
15. Binnen twee weken voorafgaand aan kapwerkzaamheden dienen alle holen, spleten en gaten te worden gecontroleerd op aanwezigheid van vaste rust- en verblijfplaatsen van uilen. De controle dient te worden uitgevoerd na raadpleging en onder begeleiding van een ter zake kundige1 op het gebied van vogels en dient met behulp van diervriendelijke methodes uitgevoerd te worden.
16. De aanleg van de werkweg en de daarmee samenhangende mitigerende maatregelen dienen te worden toegevoegd aan het actuele werkprotocol.
17. Voor de soorten waarvoor uitbreiding is aangevraagd dienen werkzaamheden, mitigerende en compenserende maatregelen in het werkprotocol te worden opgenomen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[project "Grensmaas Borgharen-Itteren, locatie Itteren" gelegen in gemeente Maastricht, gelegen ten oosten van Itteren]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0334" userIdentity="Alterra1" derogation_reference="Alterra1-B-95-2010021810564065">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-22</licenseValidFrom>
		<licenseValidUntil>2012-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
			<region code="NL31">Utrecht</region>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[De verbreding van het knooppunt Deil maakt deel uit van een in 2000 vastgesteld Tracébesluit. Voor de ecoducten moet een Tracébesluit nog worden genomen. De uitvoering van de voorgenomen verbreding en de aanleg van de ecoducten liggen daarmee (bijna) vast. Omdat het tracé waarop het Tracébesluit van toepassing is gedeeltelijk beslag legt op gronden die deel uitmaken van de Ecologische Hoofdstructuur, is een compensatieplan opgesteld. In dit plan, dat in overleg met betrokkenen uit de streek is opgesteld, zijn gronden geselecteerd waar de compensatie kan worden uitgevoerd. Het ligt in de bedoeling de vereiste compensatie gedurende de uitvoering van de verbreding te realiseren.
Het integraal verbeteren van de doorstroming van de A2, als ook de huidige knelpunten ten aanzien van de versnipperde natuurgebieden die aan weerszijden van de A2 gelegen zijn, dient meerdere doelen (verkeer en natuurmigratie). De voorgestelde mitigerende en compenserende maatregelen beperken de effecten op aanwezige beschermde soorten afdoende. De gekozen uitvoeringswijze van de voorgenomen verbreding en de aanleg van de ecoducten is daarom bevredigend. Daarnaast zullen de ecoducten een positief effect hebben op de langs de A2 gelegen natuurgebieden, daar deze met elkaar verbonden worden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
13. De bomen binnen het werkterrein dienen in de periode september-februari gekapt worden en pas nadat alle amfibieën binnen het amfibiekerend raster zijn weggevangen.
14. Het aantasten van nesten van de grote bonte specht dient buiten het broedseizoen van deze soort plaats te vinden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Het ecoduct, Autenase Kade, komt ter hoogte van kilometer 76,3, ten zuiden van de kruising van de snelweg A2 met de Autenase Kade. Het ecoduct Beesdsche Veld komt ten noorden van Beesd, ter hoogte van kilometer 82,9, één en ander zoals is weergegeven in Bijlages 1, 2 en 3 van de bij de aanvraag gevoegde projectomschrijving “Rijksweg A2, Aanleg ecoducten en "ombouw knooppunt Deil" van juli 2008.
Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[Project "A2 aanleg ecoducten" en "ombouw knooppunt Deil" in de gemeenten Vianen, Geldermalsen en Neerijnen.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0362" userIdentity="Alterra1" derogation_reference="Alterra1-B-96-2010021814414495">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2009-08-01</licenseValidFrom>
		<licenseValidUntil>2014-07-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[Er is geen alternatief voorhanden. Het handhaven van de bebouwing is niet wenselijk vanwege de nieuwe eisen die worden gesteld aan een varkensverblijf. Ook kan het eternieten dak in de toekomst een gevaar vormen voor de volksgezondheid. Daarnaast zal het bedrijf zal 12 fte. aan werkgelegenheid gaan bieden. U geeft aan zorgvuldig te werk te gaan om zo de verstoring tot een minimum te beperken. Een deel van het territorium zal verloren gaan, maar dit wordt gedeeltelijk binnen het plangebied gecompenseerd door de kwaliteit van het bestaande leefgebied te verbeteren, de akkers en weilanden in de directe omgeving blijven onveranderd. Ook wordt ruim voor de werkzaamheden een alternatieve nestplaats aangeboden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen schuur</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>2</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De maatregelen genoemd in paragraaf 6.1 van het bij de aanvraag gevoegde rapport "Flora- en faunaonderzoek voor de bouw van een zeugenhouderij en woonhuis aan de Kerkedijk 1 te Streksel" van juli 2008 dienen te worden uitgevoerd, met in achtneming van onderstaande voorwaarden.
8. De sloopwerkzaamheden dienen plaats te vinden buiten het broedseizoen, welke globaal loopt van medio maart tot juli.
9. Minimaal twee weken vóór aanvang van de sloopwerkzaamheden dient de steenuilenkast geplaatst te worden.
10. De locatie voor de nestkasten dient aan de volgende eisen te voldoen:
-  De nestkast dient te worden geplaatst in een boom die voldoende dekking en schaduw geeft.
-  De invliegopening van de nestkast dient goed bereikbaar te zijn voor de uil.
-  De nestkast dient zo ver mogelijk verwijderd van de werkzaamheden geplaatst te worden.
-  De nestkast dient niet boven of vlakbij het water geplaatst te worden.
-  De nestkast dient 2 tot 4 meter boven het maaiveld te worden geplaatst.
11. Eén week voor aanvang van de sloop van de betreffende schuur, dienen na het uitvliegen van de steenuilen alle invliegopeningen afgedicht te worden of de schuur dient gedeeltelijk opengebroken te worden zodat de vaste rust- en verblijfplaats ongeschikt wordt gemaakt. Als is vastgesteld dat er geen steenuilen meer aanwezig zijn in de te slopen schuur kan begonnen worden met de sloopwerkzaamheden.
12. Ook de overige gebouwen dienen vóór aanvang van de sloop op de aanwezigheid van steenuilen te worden gecontroleerd, omdat er een mogelijkheid bestaat dat de steenuil hierin zijn intrek heeft genomen.
13. De compensatie dient uitgevoerd te worden zoals beschreven in het compensatieplan in figuur 3 van het bij de aanvraag gevoegde rapport “ Flora- en faunaonderzoek voor de bouw van een zeugenhouderij en woonhuis aan de Kerkedijk 1 te Streksel” van juli 2008 en dient uiterlijk 2011 gereed te zijn.
14. Alle compenserende en mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van steenuilen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Bouw zeugenhouderij en woonhuis in Sterksel" gelegen aan de Kerkedijk 1 te Sterksel in de gemeente Heeze-Leende]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0367" userIdentity="Alterra1" derogation_reference="Alterra1-B-97-2010021814550198">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-23</licenseValidFrom>
		<licenseValidUntil>2013-10-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het plan Beethoven, dat deel uitmaakt van de Zuidas, behelst de ontwikkeling van kantoren, woningen, onderwijs en voorzieningen. Het project Zuidas is een grootstedelijk project met, volgens u, belang voor de hele stad. Volgens het structuurplan van Amsterdam wordt de Zuidas een toplocatie voor wonen, werken en voorzieningen, waarmee de stad zich internationaal kan profileren. Het groene karakter is van belang voor de kwaliteit van het project. Het groen dat verdwijnt ten koste van de nieuwe bebouwing in het zuidwestelijke deel van het gebied, wordt gecompenseerd door uitbreiding van het groen in het noordwestelijke deel van het plangebied waar de bebouwing definitief zal verdwijnen.
Het totale aantal vierkante meters groen blijft hierdoor gehandhaafd. De nieuwe inrichting van het groen is bovendien van een hogere kwaliteit. Er zijn geen alternatieven voorgesteld.
De voorgenomen inrichting en werkwijze zijn echter zodanig dat verstoring zoveel mogelijk voorkomen wordt en de gunstige staat van instandhouding van de grote bonte specht gewaarborgd blijft. In de omgeving van het plangebied is daarnaast voldoende alternatief leefgebied aanwezig en naar alle waarschijnlijkheid zal er op termijn in het plangebied ook weer geschikt leefgebied voor de grote bonte specht ontstaan. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden
is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de grote bonte specht, om verstoring in de meest kwetsbare periode (voortplanting) te voorkomen. De broedperiode van de grote bonte specht loopt globaal van april tot en met juni. Afhankelijk van het seizoen en de weersomstandigheden kan deze periode langer dan wel korter zijn. De geschiktheid van de periode voor het uitvoeren van de werkzaamheden, dient te worden bepaald door een ter zake kundige1 op het gebied van vogels.
8. Direct voorafgaand aan de kapwerkzaamheden dienen de bomen met nestholten van de grote bonte specht gecontroleerd te worden op de aanwezigheid van spechten. Indien er exemplaren van de grote bonte specht aanwezig zijn, dienen deze verjaagd te worden.
9. Bovenstaande mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van vogels]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Beethoven", gelegen in het zuidelijk deel van het Beatrixpark, tussen de snelweg A10, Beethovenlaan, Prinses Irenestraat en het Beatrixpark, in stadsdeel Zuideramstel in de gemeente Amsterdam]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2007/0547" userIdentity="Alterra1" derogation_reference="Alterra1-B-98-2010022721210706">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-30</licenseValidFrom>
		<licenseValidUntil>2013-02-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Tyto alba, Falco tinnunculus]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[Er is door het College en de gemeenteraad van Zwolle is een afweging gemaakt tussen verschillende belangen waarbij de keuze op Stadshagen is gevallen voor het aanleggen van een VINEX-locatie. Bij andere locaties aan de westkant van Zwolle worden grotendeels dezelfde beschermde soorten verwacht, waardoor de keus voor een ander gebied zou niet noodzakelijkerwijs beter zou zijn geweest. De wijk Stadshagen II sluit ruimtelijk aan bij Stadshagen I en is vastgelegd in het Structuurplan Stadshagen II en uitgewerkt in het bestemmingsplan Stadshagen II en de Milieueffectrapportage Stadshagen II. De kaders en ambities uit deze plannen zijn functioneel, ruimtelijk en financieel verder uitgewerkt in een Masterplan Stadhagen II, waarin harde uitgangspunten zijn opgenomen met betrekking tot de in het gebied aanwezige ecologische waarden. Deze uitgangspunten zijn:
- Het vrijhouden of maken van migratiezones voor dieren tussen het Zwarte Meer, de Polder Mastenbroek en de IJssel.
- Het voorkomen van verlies aan natuurwaarden.
- De compensatie van het verlies aan natuurwaarden in of buiten Stadhagen II.
- Het toepassen van natuurvriendelijke oevers in groengebieden.
- Het beperken van het ophogen van groene gebieden.
- Het beperken van hoge boombeplanting aan de polderzijde in verband met weidevogelwaarden in de polder.
Inrichting en werkwijze van het project zijn zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding blijft gewaarborgd.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen, slopen gebouwen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>7</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>5</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>5</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[Voor de buizerd komt de gunstige staat van instandhouding niet in het geding  De gunstige staat van instandhouding van de buizerd, kerkuil en de torenvalk komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De ontheffinghouder dient bij de planning van de werkzaamheden rekening te houden met de seizoensactiviteiten van de soort(en) waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (voortplanting, winterrust) te voorkomen.
8. Het verlies aan jachtgebied voor de torenvalk en de kerkuil dient te worden gecompenseerd. Hiertoe dient een deel van de nieuwe groenstroken en randzones van Stadshagen II zodanig worden ingericht en beheerd dat hierin permanent plaats is voor  veldmuizenpopulaties.
9. Indien het bouwrijp maken van percelen in het broedseizoen moet plaatsvinden, dienen voorbereidende maatregelen getroffen te worden om te voorkomen dat vogels tot broeden kunnen komen binnen het plangebied. Deze vogelwerende maatregelen, zoals het plaatsen van roodwitte linten, moeten voorafgaand aan het broedseizoen worden genomen, waarbij het terrein kort voor de uitvoering door een ter zake kundige1 moet worden onderzocht op de aanwezigheid van broedvogels.
10. Indien blijkt dat er vogels op het terrein broeden, dienen er maatregelen te worden genomen om te zorgen dat de nesten niet worden verstoord. Bij weidevogels mag binnen een straal van 75 meter rond het nest niet gewerkt worden, zolang het nest nog in gebruik is. Deze zone dient duidelijk zichtbaar gemaakt te worden voor de uitvoerders, bijvoorbeeld door middel van piketpaaltjes.
11. Werkzaamheden waarbij vaste verblijfplaatsen (nesten) en belangrijke jachtgebieden van buizerd, torenvalk en kerkuil worden aangetast, moeten buiten het broedseizoen worden uitgevoerd.
12. De sloop van boerderijen waarin zich vaste verblijfplaatsen van kerkuilen bevinden, mag pas plaatsvinden nadat uit onderzoek is gebleken dat de boerderijen geen functie hebben als vaste verblijfplaats voor vleermuizen.
13. Op geschikte locaties zo dicht mogelijk in de buurt van de oude broedlocaties dienen voor de torenvalk tenminste 8 en voor de kerkuil tenminste 4 nestkasten te worden geplaatst]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Ininrichting Stadshagen II" in de gemeente Zwolle]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2005/0038" userIdentity="Alterra1" derogation_reference="Alterra1-B-99-2010022721470686">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-31</licenseValidFrom>
		<licenseValidUntil>2013-01-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[U heeft in de door u op 7 januari 2005 ingediende ontheffingsaanvraag met kenmerk FF/75C/2005/0003 al aannemelijk gemaakt dat alternatieve locaties en werkwijzen ongeschikt zijn. De destijds gemaakte beoordeling acht ik nog steeds valide. Er is derhalve voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
10. Behoudens de bomen en houtopstanden binnen het werkgebied van fase 1, welke gekapt mogen worden in de periode tot en met 31 december 2008, dient het kappen van bomen en struiken tussen 15 september en 1 november plaats te vinden, omdat dit de minst ongunstige periode voor de betreffende soorten is. Dit dient te worden uitgevoerd onder begeleiding van een ter zake kundige1.
11. Aangezien de ontheffing meer dan twee jaar van tevoren wordt afgegeven, is het mogelijk dat de omstandigheden in het plangebied veranderd zijn tegen de tijd dat de werkzaamheden gestart zullen worden of tijdens de uitvoering van de werkzaamheden zullen veranderen. Om overtreding van verbodsbepalingen van de Flora- en faunawet te voorkomen en aan de zorgplicht te voldoen, is het noodzakelijk om voorafgaand aan de werkzaamheden het gehele plangebied opnieuw te inventariseren, in een daarvoor geschikte periode. Verder dient het gebied tijdens de uitvoering van de werkzaamheden te worden gemonitord. Voor eventueel nieuw aangetroffen soorten dient alsnog aanvullend ontheffing te worden aangevraagd. Van deze monitoring dient een rapportage te worden opgesteld.
Daarnaast dient een voortgangsrapportage van het project te worden opgesteld, met daarin opgenomen de werkzaamheden, de fase van uitvoering, de genomen voorzorgsmaatregelen en de compenserende/mitigerende maatregelen. Deze rapportages dienen ter beoordeling aan Dienst Regelingen te worden gezonden. De eerste voortgangsrapportage met de voorafgaande inventarisatie uit 2007 dient eind 2008 te worden toegezonden. Eind 2010 dient u een tweede rapportage te versturen.
In 2013 bij de afronding van het project dient de eindrapportage met alle genomen mitigerende en compenserende maatregelen te worden toegestuurd]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het project "Combiplan Nijverdal", dat zal worden uitgevoerd in Nijverdal, gemeente Hellendoorn]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2006/0090A" userIdentity="Alterra1" derogation_reference="Alterra1-B-100-2010022721570555">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-10-31</licenseValidFrom>
		<licenseValidUntil>2011-04-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL41">Noord-Brabant</region>
		</regions>
		<alternativesAssessed><![CDATA[In het kader van uw oorspronkelijke ontheffingsaanvraag voor het project ‘Zuiderklip: polder Moordplaat fase 2’ met kenmerk FF/75C/2006/0090 is de noodzaak van het beëindigen van de landbouwactiviteiten, de waterpeilverlaging en de natuurontwikkeling in het gebied al voldoende onderbouwd. Voor de overwegingen die tot die conclusie hebben geleid verwijs ik u naar mijn besluit van 31 augustus 2008. In de tweede fase van het project worden een landbouwschuur, een werkkeet en een zomerhuisje gesloopt.
De gebouwen bevinden zich op polderniveau en zouden na afronding van het project onder water komen te staan. De sloop is nodig om een optimale doorstroming in het gebied te realiseren, die nodig is in het kader van de doelstellingen van het programma Ruimte voor de Rivier. Hiermee is het voldoende aangetoond dat geen bevredigend alternatief voor deze aanvullende ingrepen voorhanden is. De compenserende en mitigerende maatregelen ten behoeve van de ruige dwergvleermuis en de kerkuil zijn voldoende om de gunstige staat van instandhouding van deze soorten te waarborgen.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen met nestplaats</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de kerkuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
10. Ter compensatie van het verlies van de nestlocatie van de kerkuil dient een uilenkast te worden opgehangen op een voor de soort bereikbare plek in de nabijheid van locatie A.
11. Bij de planning van de (sloop)werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de ruige dwergvleermuis en de kerkuil om verstoring in de meest kwetsbare perioden te voorkomen. Ten aanzien van de ruige dwergvleermuis houdt dit in dat gesloopt dient te worden in de periode eind maart-april of oktober-medio november. Voorafgaande aan de sloop van de betreffende werkkeet en het zomerhuisje dienen de beide gebouwen te worden gestript om het microklimaat te verstoren. De sloop kan beginnen nadat de betreffende gebouwen aan een laatste inspectie zijn onderworpen en geconcludeerd is dat de aanwezigheid van vleermuizen kan worden uitgesloten. Ten aanzien van de kerkuil houdt dit in dat voorafgaande aan de sloop van de betreffende
landbouwschuur een controle plaats dient te vinden naar de aanwezigheid van de soort in de schuur. De sloop van de betreffende schuur mag pas plaatsvinden nadat de afwezigheid van de soort is bevestigd. Dit houdt in dat er geen broedsel (meer) aanwezig is en er geen jongen aanwezig zijn die nog niet vliegvlug zijn.
12. Alle bovengenoemde maatregelen dienen te worden uitgevoerd door en/of onder begeleiding van een deskundige1 op het gebied van de soorten waarvoor deze ontheffing is verleend.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het gebied de "Zuiderklip", deelgebied de Moordplaat, gelegen in de Brabantse Biesbosch]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0379" userIdentity="Alterra1" derogation_reference="Alterra1-B-101-2010022722121320">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-06</licenseValidFrom>
		<licenseValidUntil>2013-10-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL32">Noord-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[Het Ministerie van Volksgezondheid, Welzijn en Sport heeft als beleid, minder validen beter te integreren in de maatschappij. Binnen de planlocatie kan dit worden gerealiseerd door zowel woningen voor de reguliere markt, als voor de Prinsenstichting, een organisatie die zorg, ondersteuning en woonruimte biedt aan (verstandelijk) gehandicapten, te bouwen. Het project past in de structuurvisie van de gemeente Purmerend (structuurplan 2006-2020), waarin de gemeente wil investeren in ‘bloei in plaats van groei’. Het plan leidt in ecologisch opzicht per saldo tot een verbetering. Ook sluit het project aan op het streekplan Noord-Holland Zuid 2003, door in te spelen op de behoefte aan een groen woonmilieu en het beleid wonen en zorg. Voor de realisatie van het project hebben de Prinsenstichting, de gemeente Purmerend en de Woningstichting Rochdale een samenwerkingsovereenkomst gesloten. Het project heeft druk op de beschikbare ruimte in het plangebied tot gevolg en dit heeft na een zorgvuldige afweging geleid tot inperking van de groene randzone. Het dempen van delen van de inhammen in de watergangen aan de noordzijde van het plangebied is nodig om aan de watertoets te kunnen voldoen. Op de planlocatie zijn reeds gebouwen van de Prinsenstichting aanwezig, welke niet meer voldoen aan de wettelijke eisen. Voor nieuwbouw binnen de stedelijke omgeving was geen ruimte en nieuwbouw elders zou ten koste gaan van landelijk gebied met waarschijnlijk hogere natuurwaarden. Het project is daarmee plaatsgebonden. Er is bij de afweging van inrichtingsalternatieven rekening gehouden met de toekomstige natuurwaarden in het gebied. Inrichtingsalternatieven voor het geplande bouwproject leverden echter een grotere aantasting van de doorgaande groene randzone (‘gemeentelijk ecozone’) op. Uitgangspunt bij het inrichtingsplan is geweest dat de groene uitstraling van het gebied behouden zou blijven. Het aantal bomen dat behouden blijft zal echter beperkt zijn door de nieuwe indeling van het terrein en de noodzakelijk ophoging. Een groot aantal bomen zal worden aangeplant. Het is echter niet duidelijk of de effecten op de aanwezige beschermde soorten zijn overwogen bij de locatie- en inrichtingskeuze. Door de geplande ophoging van het terrein en de indeling van de nieuwe woningen verdwijnt een groot areaal groen, dat op dit moment van belang is voor grote bonte specht en als foerageergebied en verblijfplaats van een aantal vleermuissoorten. Voor deze beschermde soorten is het beter om een zo groot mogelijk areaal groen te behouden. Indien evenwel de door u en de aan de ontheffing verbonden compenserende en mitigerende maatregelen uitgevoerd worden, wordt er zorgvuldig gehandeld en komt de gunstige staat van instandhouding van de beschermde soorten niet in het geding. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>2</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen zoals beschreven in de hoofdstukken 7 en 8 van de bij de aanvraag gevoegde ‘Projectomschrijving “Kwadijkerpark, Gemeente Purmerend”. Locatie: Purmerkoog, gemeente Purmerend, Provincie Noord-Holland’ dienen te worden uitgevoerd met inachtneming van de onderstaande voorwaarden.
11. Er dienen geen bomen te worden gekapt tijdens de paarperiode van ruige dwergvleermuis. Deze periode loopt globaal van half augustus tot en met half oktober.
12. Direct voorafgaand aan de kapwerkzaamheden dienen alle mogelijke vaste rust- en verblijfplaatsen (holten, spleten en dergelijke) te worden gecontroleerd op de aanwezigheid van exemplaren van de ruige dwergvleermuis. Indien noodzakelijk voor uitsluiting van bewoning dient dit met behulp van een camera, verrekijker, spiegel, danwel met behulp van sporenonderzoek (keutels, urine, meststrepen, vlindervleugelresten, etc.) te worden nagegaan]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande
organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap,
KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[het gebied de "Kwadijkerpark" in gemeente Purmerend. Het betreft de locatie Spinnekop 5, 1440 CC te Purmerend,]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0067" userIdentity="Alterra1" derogation_reference="Alterra1-B-102-2010022722291852">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-14</licenseValidFrom>
		<licenseValidUntil>2013-02-18</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Falco subbuteo, Buteo buteo, Picus viridis, Dendrocopos major, Asio otus, Accipiter nisus]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[In de planvorming van het project Nieuwe Hollandse Waterlinie is onderzocht waar geschikte locaties aanwezig zijn om een voorbeeldproject te realiseren. Hierbij is onder andere gekozen voor het project “Herinrichting Molenkade”. Argumenten voor de keuze van de locatie Molenkade zijn:
·  De combinatiemogelijkheden met de ecologische verbindingszone en de waterbergingopgave;
·  De mogelijkheid om benodigde waterberging en de visualisatie van inundatievelden te combineren;
·  De beleefbaarheid van de Nieuwe Hollandse waterlinie vanaf de Rijksweg A2;
·  De beleefbaarheid van de Nieuwe Hollandse waterlinie vanaf de Diefdijk;
·  De combinatie met het viaduct van de Diefdijk over de A2. Dit viaduct heeft zowel een verkeerskundige als een waterkerende functie (kan afgesloten worden);
·  De aanwezigheid van een Kanonkazemat aan de noordzijde van de A2;
·  De aanwezigheid van diverse bunkers (groepsschuilplaatsen) die een zichtbaar element zijn van de waterlinie;
·  De eigendomssituatie, die realisatie ter plekke mogelijk maakt.
Het plan is om de Nieuwe Hollandse Waterlinie aan beide zijden van de Rijksweg A2 zichtbaar te maken. Omdat de verwerving van gronden aan de noordzijde tot op heden niet is gelukt, beperkt het project zich vooralsnog tot werkzaamheden aan de zuidzijde
van de A2.
In opdracht van de gemeente Culemborg is het Voorlopig Technisch Ontwerp opgesteld (VTO). Dit VTO is gepresenteerd tijdens een inloopdag in februari 2007. Tijdens en na deze inloopdag zijn diverse reacties binnen gekomen. Eén van de reacties bestond uit een alternatief plan dat bij brief van 27 januari 2007 is ingediend door een groep ecologen. Deze reacties, in combinatie met het beschikbaar komen van de Natuurtoets Molenkade, hebben geleid tot een hernieuwde alternatievenafweging. Hierbij zijn de alternatieven beoordeeld op de effecten op de beschermde ecologische waarden en op de eisen die vanuit de doelstellingen van het project zijn gesteld. Hierbij zijn alternatieven beoordeeld, waaronder het ‘ecologen alternatief’. De invloed van de voorgenomen maatregelen op de bestaande natuurwaarden is nadrukkelijk meegenomen. Gekozen is voor een alternatief dat de natuurwaarden beduidend minder aantast dan het oorspronkelijke VTO en gelijktijdig de overige doelstellingen in voldoende mate realiseert. Dit heeft geleid tot het Definitieve Ontwerp (DO). Hierbij is met name gekeken naar de mogelijkheden om de ecologisch
waardevolle bosgebieden in stand te houden. Op de boslocatie direct tegen de A2 aan na, worden deze allemaal gespaard. Met de instandhouding van het bos wordt bedoeld het handhaven van de oude bosbodem met zijn natuurlijke begroeiing en niet het
handhaven van de kaprijpe populierenbestanden die met een productiedoel zijn aangeplant.
De verschillen in de ecologische effecten van het DO ten opzichte van het VTO zijn gelegen in het behoud van een belangrijk deel van de oudere boslocaties. Het ‘ecologen alternatief’ kent minder negatieve effecten, met name op de broedvogels, maar is afgevallen omdat het naar het oordeel van de projectgroep niet voldoet aan de doelstellingen van het plan. Zichtlijnen in het bos vanaf Diefdijk en A2 worden door dit alternatief onderbroken.
Het DO heeft naar verwachting duidelijk positieve effecten op de heikikkerpopulatie door de realisatie van meer voortplantingsbiotoop. Ook voor de bittervoorn, grote modderkruiper en de kleine modderkruiper zullen naar verwachting positieve effecten hebben op de populatie in het plangebied. In het zuidelijke deel van het gebied zijn belangrijke positieve effecten te verwachten door de ontwikkeling van zeldzaam nat schraalland.
Voor wat betreft de zichtlijnen wordt onderscheid gemaakt tussen de zichtlijnen vanaf de Rijksweg A2 en de zichtlijnen vanaf de Diefdijk. Vanwege de hoogteligging van de Diefdijk is het goed mogelijk om over een griend begroeiing heen te kijken. De aanwezige populierenbeplanting vormt wel een visuele barrière. Daarom is er voor gekozen om geen griend langs de A2 aan te brengen, maar wel in de rest van het gebied. Vanaf de Rijksweg A2 vormt griend eveneens een visuele barrière. Doel van het plan is om de Diefdijk met
zijn ‘bunkers’ met daarvoor het water van de Nieuwe Hollandse waterlinie zichtbaar te maken. Het creëren van doorkijklijnen in de vorm van smalle open stroken in het bos geeft niet het gewenste effect van het zichtbaar maken van de wijdheid van de  inundatievlakte. Dit aspect is bij de afweging van alternatieven ook aan de orde geweest.
Het VTO is op enkele punten aangepast, zodat in het DO meer rekening is gehouden met de aanwezigheid van strikt beschermde soorten. Uitvoering van het DO zal echter nog steeds leiden tot negatieve effecten op deze beschermde soorten. De gekozen inrichting wordt echter verantwoord door het maatschappelijk belang welke hieronder wordt behandeld.
Ten behoeve van het project moet onder andere bos gekapt worden en een bunker aangepast worden. Er worden voldoende mitigerende en compenserende maatregelen getroffen, zodat op een zorgvuldige wijze de werkzaamheden worden uitgevoerd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>8</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>8</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>10</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht, grote bonte specht en de sperwer komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
Algemeen
7. Bij de planning van de werkzaamheden dient rekening te worden gehouden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare periode (voortplanting en overwintering) te voorkomen. Afhankelijk van het seizoen en de weersomstandigheden kunnen deze perioden langer dan wel korter zijn. De geschiktheid van de periode voor het uitvoeren van de werkzaamheden dient te worden bepaald door een deskundige1 op het gebied van de soort waarvoor ontheffing wordt verleend.

Werkzaamheden in bos en griend (ten behoeve van amfibieën en broedvogels)
23. De bomen dienen met een motorzaag gekapt te worden in de periode september-half februari. De stobben dienen in de periode half februari tot en met half maart verwijderd te worden, in verband met het broedseizoen van vogels. De op de grond liggende boomstammen dienen bij voorkeur verwijderd te worden in de periode buiten de overwinteringsperiode van de heikikker, omdat door het
uitrijden van de boomstammen de grond wordt verstoord (en daarmee de hierin overwinterende heikikkers).
Broedvogels
28. De bomen met nesten van roofvogels, spechten en uilen dienen gekapt te worden buiten het broedseizoen.
Werkprotocol
29. Alle bovenstaande compenserende en mitigerende maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[De elzenbossen met populieren in het plangebied vormen een broedplaats voor de boomvalk, buizerd (2 paren), groene specht, grote bonte specht (4 paren), ransuil en de sperwer.

1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Herinrichting Molenkade" in de gemeente Culemborg. Het projectgebied ligt tussen de Rijksweg A2, de Diefdijk en de Culemborgse Vliet]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0184" userIdentity="Alterra1" derogation_reference="Alterra1-B-103-2010022820554623">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-14</licenseValidFrom>
		<licenseValidUntil>2013-08-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Strix aluco, Buteo buteo, Dendrocopus major]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[Het voorkeursmodel uit de Nota van uitgangspunten ontwikkeling Wissinkbrink uit 2007 is gebaseerd op het Structuurplan Haaksbergen 2015 uit 2006. In dit plan wordt richting gegeven aan de ruimtelijke ontwikkeling van het stedelijk gebied van de gemeente Haaksbergen. In de Nota wordt uitgegaan van de realisatie van 498 woningen aan de Wissinkbrink.
Het gemeentelijk beleid ten aanzien van wonen is verwoord in de Woonvisie 2003+. Het woningaanbod in de gemeente is onvoldoende afgestemd op starters en ouderen, terwijl de verwachting is dat die groepen woningzoekenden de komende tien jaar in omvang zullen toenemen. In het Streekplan staat aangegeven dat de uitbreiding voornamelijk moet plaatsvinden tussen het toekomstige tracé voor de Twenteroute en de kern van Haaksbergen. De Wissinkbrink past goed binnen deze voorwaarden. De Eibergsestraat vormt een zwaarwegende belemmering voor de uitbreiding aan de zuid- en zuidoostzijde van de kern. De Twenteroute (N18) en de natuurgebieden ten oosten en zuiden van Haaksbergen vormen een beperking voor uitbreiding van Haaksbergen in zuidelijke en oostelijke richting kan plaatsvinden. Realisatie in deze richting zal tot vergelijkbare of meer negatieve effecten leiden. Het project is hiermee plaatsgebonden. De inrichting en werkwijze zijn zodanig voorgesteld dat verdere verstoring zoveel mogelijk wordt voorkomen en de gunstige staat van instandhouding verder gewaarborgd blijft. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen, aantasting leefgebied</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>5</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>5</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>7</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de bosuil, buizerd, groene specht, steenuil en torenvalk komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
15. Het aantasten van het steenuilnest dient plaats te vinden in de periode oktober-januari. Ten aanzien van andere broedvogels dient buiten het broedseizoen gewerkt te worden.
16. Voor de bosuil en de torenvalk dienen voorafgaand aan de verstorende werkzaamheden per soort 2 nestkasten te worden opgehangen. Van belang is dat de nieuwe nestkasten niet in bestaande territoria van andere exemplaren van de soorten geplaatst worden.
17. De compenserende maatregelen ten aanzien van de steenuil dienen te worden uitgevoerd conform het bij de aanvraag gevoegde ‘Compensatieplan Steenuil Wissinkbrink Haaksbergen’ van 10 september 2008 en uw e-mail met onderwerp ‘RE: steenuilen Haaksbergen’ van 9 oktober 2008. Indien op een nieuwe nestlocatie niet voldoende foerageergebied aanwezig is, dan dienen de aanvullende compenserende maatregelen getroffen te worden (aangepast beheer, takkenrillen, muizenruiters), zoals in het compensatieplan beschreven is.
18. Bij de compenserende maatregelen ten aanzien van de steenuil dient rekening gehouden te worden met het toekomstige tracé van de N18 ten noorden van Haaksbergen.
19. De nestresultaten en het territoriumgebruik van de steenuil in het plangebied dienen gedurende het aankomende voortplantingsseizoen geobserveerd te worden. Uit de gegevens dient te kunnen worden opgemaakt of de steenuilen die in het gebied zijn aangetroffen één van de alternatieve leefgebieden accepteren of dat er een lichte verschuiving van territoria plaatsvindt. De resultaten dienen eind 2009 aan Dienst Regelingen te zijn doorgegeven. Naar aanleiding van deze gegevens kunnen eventueel aanvullende maatregelen worden opgelegd.
20. Alle bovenstaande werkzaamheden dienen te worden uitgevoerd onder begeleiding van een deskundige1 op het gebied van de soort waarvoor ontheffing is verleend.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[De elzenbossen met populieren in het plangebied vormen een broedplaats voor de boomvalk, buizerd (2 paren), groene specht, grote bonte specht (4 paren), ransuil en de sperwer.

1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Wissinkbrink Haaksbergen" in de gemeente Haaksbergen. Het betreft het gebied aan de noordzijde van de dorpskern van Haaksbergen]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0250" userIdentity="Alterra1" derogation_reference="Alterra1-B-104-2010022821144412">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-14</licenseValidFrom>
		<licenseValidUntil>2010-06-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL33">Zuid-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[In 2002 heeft het kabinet Balkenende I in zijn visie over ruimtelijke ordening naar voren gebracht. Uit deze visie blijkt onder meer een voorkeur voor bouwen binnen bestaande stedelijke kernen, boven bouwen in het buitengebied. Het plangebied, dat binnen de bebouwde kom van Alphen aan den Rijn ligt, valt in het streekplan Zuid-Holland Oost dan ook binnen de ‘bebouwingscontour’. In de gemeentelijke welstandsnota van 2004, het gemeentelijk verkeers- en vervoerplan en ook in de Regiovisie Rijnstreek plus uit 2002 worden de mogelijkheden van het gebied nader uitgewerkt, waarbij de functies wonen, zorg, werken, recreëren en vervoer de belangrijkste componenten vormen. Doel van project Nieuwe Sloot is te komen tot een duurzame invulling van het gebied Nieuwe Sloot, door middel van een uitgebalanceerde toevoeging van nieuwe woningen aan de bestaande voorraad, in combinatie met een kwalitatieve invulling van de omgeving. Voor de woningen wordt gestreefd naar grote differentiatie in woontypologieën. Een afweging op ecologische gronden voor de inrichting van het plangebied heeft niet plaatsgevonden. De werkwijze is echter zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen.
Er wordt voldoende gemitigeerd om de gunstige staat van instandhouding van aanwezige beschermde soorten te waarborgen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
10. Alle bovenstaande maatregelen dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van vogels.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[Onder een ter zake kundige wordt verstaan een persoon die:
·  Op HBO, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie en/of
·  Als ecoloog werkzaam is voor een ecologisch adviesbureau dat is aangesloten bij het netwerk Groene Bureaus en/of
·  Zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij de daarvoor in Nederland bestaande organisaties (zoals Das en Boom, VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, VOFF, SOVON, etc.)]]></comments>
		<location><![CDATA[Project "Nieuwe Sloot" in de gemeente Alphen aan den Rijn. Het betreft drie deelgebied in Alphen aan den Rijn.]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0338" userIdentity="Alterra1" derogation_reference="Alterra1-B-105-2010022821301470">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-11</licenseValidFrom>
		<licenseValidUntil>2009-02-28</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis, Dendrocopos major, Dryocopus martius]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Het realiseren van een fietspad langs de N820 is een onderdeel van het Uitwerkingsplan Winterswijk-Oost. Onderdeel van het plan is het verhogen van de verkeersveiligheid. Eén van de maatregelen voor het bevorderen van de verkeersveiligheid is het realiseren van een vrijliggende fietsverbinding langs de weg, tussen Winterswijk en Vreden. In de huidige situatie zijn fietsstroken onderdeel van de weg. De fietsverbinding wordt als onveilig ervaren. Een vrijliggend fietspad zal ook bijdragen aan het verbeteren van de toeristische routestructuur in het gebied. Een vrijliggend fietspad waarbij de bomen worden gespaard is niet mogelijk. Ten eerste dient volgens het provinciale verkeersveiligheidbeleid een obstakelvrije zone van 2,5 meter aangehouden te worden bij 60-kilometerwegen. Dit beleid geldt voor aanleg van nieuwe wegen en voor reconstructie van bestaande wegen. Dit laatste is hier het geval. Ten tweede is de bereidheid tot de verkoop van gronden door grondeigenaren bepalend voor het tracé en het profiel van de middenberm (tussen rijbaan
en fietspad). Er kon niet méér grond worden aangekocht dan noodzakelijk voor het minimale profiel, dat volgt uit het ‘Handboek Wegontwerpen’ en de Gelderse Essentiële Wegkenmerken. Landgoedeigenaren stonden doorsnijdingen van hun landgoederen niet toe, vanwege het nadelige gevolg daarvan op de rangschikkingen betreffende de Natuurschoonwet. Met de kap van 512 bomen langs de Vredenseweg volgens de oorspronkelijke
aanvraag, verdwijnen voor een aantal beschermde vleermuissoorten een groot oppervlak belangrijk foerageergebied en een belangrijke vliegroute.
Het alternatief waarbij 287 bomen worden gekapt is beter, niet alleen omdat een geringer oppervlak foerageergebied verdwijnt, maar ook omdat het doorgaande karakter van de vliegroute op lange termijn gehandhaafd blijft. Door herplant en het gebruik van geschikte bomen (beuken en zomereiken) zal het foerageergebied zich op termijn herstellen. De keus voor wat grotere boompjes (handelsmaat 14-16) bespoedigt het herstel. Bij het alternatief
zijn inrichting en werkwijze zodanig voorgesteld dat verstoring zoveel mogelijk wordt voorkomen. De gunstige staat van instandhouding blijft gewaarborgd. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
			<activity code="82">Deliberate disturbance during the period of rearing</activity>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
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			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de Groene specht, grote bonte specht en zwarte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
12. De herplant van de bomen dient plaats te vinden zoals staat aangegeven op de kaarten 1 tot en met 4 van 10 april 2007 bij de brief van C.F. van Heteren van 13 oktober 2008. In plaats van wintereiken dienen zomereiken en beuken te worden geplant.
13. Bij de herplant dient gebruik gemaakt te worden van zomereiken en beuken met een minimale handelsmaat van 14 tot 16 centimeter.
14. Een deskundige1 op het gebied van bomen dient de herplant te leiden. Deze dient per plaats te beoordelen welke boomsoort het meest geschikt is en hoeveel bomen er geplant dienen te worden voor het beste resultaat op de lange termijn. Hierbij mag enigszins afgeweken worden van het aantal op de kaarten genoemde aantal van 270 te herplanten bomen, als dat ten goede komt aan het doel, namelijk het op lange termijn waarborgen van de doorgaande structuur van de bomenrij.
15. Bij de werkzaamheden dienen maatregelen te worden genomen zodat de bestaande bomen niet beschadigd worden. Ook dient wortelschade zoveel mogelijk beperkt te worden.
16. De herplant dient vóór 1 februari 2010 te zijn afgerond.
17. Gedurende minimaal vijf jaar na de herplant dient nazorg te worden gepleegd aan de bomen, waarbij uitval van jonge boompjes dient te worden gecompenseerd.
18. Er dienen maatregelen genomen worden om zonnebrand aan te handhaven beuken te voorkomen.
19. Alle bovenstaande maatregelen met betrekking tot de herplant van bomen dienen onder begeleiding van een deskundige1 op het gebied van bomen plaats te vinden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[De elzenbossen met populieren in het plangebied vormen een broedplaats voor de boomvalk, buizerd (2 paren), groene specht, grote bonte specht (4 paren), ransuil en de sperwer.

1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Reconstructie N820", in de gemeente Winterswijk]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0370" userIdentity="Alterra1" derogation_reference="Alterra1-B-106-2010022821565616">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-12</licenseValidFrom>
		<licenseValidUntil>2011-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Tyto alba]]></species>
		<regions>
			<region code="NL31">Utrecht</region>
		</regions>
		<alternativesAssessed><![CDATA[De huidige bebouwing verkeert in zeer slechte staat en enkele bijgebouwen staan op instorten. Verbouwen of restaureren is niet aan de orde. De enige mogelijkheid om bewoning op de lange termijn mogelijk te maken is om nieuwbouw te plegen. U wilt het plangebied voor bewoning geschikt houden en de mogelijkheid om de te slopen panden niet te vervangen is om die reden voor u geen alternatief. Er zijn bovendien geen alternatieven mogelijk met minder negatieve effecten op de gewone dwergvleermuis en de kerkuil. Ook bij sloop zonder vervangende nieuwbouw gaan de vaste rust- en verblijfplaatsen voor de gewone dwergvleermuis en de kerkuil verloren. Het project is daarmee plaatsgebonden. Als gevolg van het project worden vaste rust- en verblijfplaatsen van beschermde soorten vernietigd. Er wordt echter zorgvuldig gehandeld ten aanzien van de gewone dwergvleermuis en de kerkuil, en de gunstige staat van instandhouding van de soorten blijft gewaarborgd, mits u voldoet aan de aan deze ontheffing verbonden voorwaarden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen gebouwen met nestplaats</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de kerkuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen zoals omschreven op pagina 5 van de bij de aanvraag gevoegde ‘Projectomschrijving Planlocatie Gelders Benedeneind 23, Veenendaal’ dienen te worden uitgevoerd met inachtneming van de onderstaande voorwaarden.
8. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (overwinterings-, paar- en kraamperioden) te voorkomen.
10. Er dienen twee tot vijf nestkasten te worden geplaatst op geschikte locaties bij boerderijen in de nabije omgeving. Een deskundige1 op het gebied van de kerkuil dient te bepalen welke locaties geschikt zijn. Hierbij dient rekening te worden gehouden met eventuele omringende bezette territoria en beschikbaarheid van prooien.
11. Als de kerkuil toch tot broeden komt dient de sloop van de schuur te worden uitgevoerd buiten het broedseizoen van de kerkuil. Een ter zake kundige1 dient te bepalen wanneer geen sprake (meer) is van broedgerelateerde activiteiten van de kerkuil in de schuur.
12. Mochten vleermuizen en/of kerkuilen worden aangetroffen tijdens de werkzaamheden, dan dienen de werkzaamheden te worden gestaakt tot de betreffende exemplaren uit eigen beweging het pand hebben verlaten.
13. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een deskundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Gelders Benedeneind 23, Veenendaal" in de gemeente Veenendaal. De planlocatie omvat een woonhuis, zeven schuren en enkele grasveldjes aan de Gelders Benedeneind 23, 3907 KX te Veenendaal]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-21</licenseValidFrom>
		<licenseValidUntil>2013-02-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Buteo buteo, Falco tinnunculus]]></species>
		<regions>
			<region code="NL21">Overijssel</region>
		</regions>
		<alternativesAssessed><![CDATA[Uit de in 2003 door de gemeente Zwolle vastgestelde nota van uitgangspunten "Hessenpoort 2" blijkt dat in de gemeente behoefte is aan uitbreiding van het oppervlak bedrijventerrein met aantrekkingskracht op bovenprovinciaal en - regionaal opererende middelgrote
en grote bedrijven. Een dergelijk terrein zal voorzien in groei van werkgelegenheid in de regio. Bij het zoeken naar een geschikte locatie zijn onder meer selectiecriteria gehanteerd:
- Het behoud van de openheid van het landschap.
- Het beschermen van archeologische waarden.
- Het sparen van kenmerkende flora- en fauna.
- Goede ontsluiting.
- Goede verbinding met bestaand bedrijventerrein.
De uiteindelijke contouren waarbinnen het nieuwe bedrijventerrein wordt ingericht, zijn tot stand gekomen op basis van een breed scala van selectiecriteria. Het alternatief dat het sterkst is gericht op behoud van natuur- en landschapswaarden is gelegen direct ten oosten van Hessenpoort I. Deze locatie licht echter buiten de grenzen van de gemeente Zwolle en is om die reden niet haalbaar. Locaties aan de noordzijde van Zwolle zijn ongunstig vanwege uitbreiding van woongebieden.
Locaties aan de zuidzijde van Zwolle zijn ongunstig vanwege de ligging van de Ecologische Hoofdstructuur. Het gekozen alternatief is om een aantal redenen gunstig:
- De locatie sluit aan op het terrein Hessenpoort I, wat kostenbesparing oplevert bij de aanleg van nutsvoorzieningen, infrastructuur en andere gedeelde voorzieningen en bedrijven kansen biedt op samenwerking.
- De locatie biedt goede mogelijkheden voor aansluiting op snelweg- en spoorinfrastructuur.
- De locatie levert relatief weinig beperkingen op van ecologische, cultuurhistorische, archeologische en bodemkundige aard.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>3</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de buizerd en de torenvalk komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De compenserende en mitigerende maatregelen zoals omschreven op pagina 12, 13 en 14 van de bij de aanvraag gevoegde ‘Projectomschrijving inrichting Hessenpoort II’ van 7 februari 2008 dienen te worden uitgevoerd met inachtneming van onderstaande voorwaarden.
8. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (voortplanting, winterrust) te voorkomen.
11. Het kappen van de bomen met de nesten van de buizerd en de torenvalk dient plaats te vinden in de periode augustus-februari. Daarnaast dient een deskundige1 op het gebied van vogels voorafgaand aan het wegnemen van de nesten te controleren op de aanwezigheid van broedende vogels en jongen.
Indien dit het geval is, dient gewacht te worden met het wegnemen van de nesten totdat de jongen vliegvlug zijn.
12. Ten aanzien van de torenvalk dienen door een deskundige1 op het gebied van vogels minimaal 2 nestkasten opgehangen te worden in de directe omgeving. Hierbij dient rekening gehouden te worden met de aanwezigheid van geschikt foerageergebied in de omgeving van de nieuwe nestkast.
13. Alle bovenstaande werkzaamheden dienen te worden uitgevoerd onder begeleiding van een deskundige1 op het gebied van de soorten waarvoor ontheffing geldt.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Hessenpoort II", in de gemeente Zwolle]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0427" userIdentity="Alterra1" derogation_reference="Alterra1-B-108-2010022822185716">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2009-02-10</licenseValidFrom>
		<licenseValidUntil>2011-02-05</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Uitgangspunt van het plan is de bouw van een nieuwe bedrijfswoning aan de Broekstraat 3 te Hummelo. In de gemeente Broeckhorst wordt het principe ‘Rood voor Rood’ toegepast, dat inhoudt dat nieuwbouw alleen plaatsvindt wanneer er bestaande gebouwen worden gesloopt. Onder deze voorwaarde wordt nieuwbouw in de gemeente toegestaan.
De schuren in deelgebied Lendebosch 3 zullen onder voortzetting van het huidige beheer en onderhoudsniveau op den duur in verval raken en ook voor de steenuil ongeschikt worden. De schuur met daarin de steenuilroestplaats heeft geen economische functie, wordt niet onderhouden en zal op termijn ongeschikt worden voor de steenuil. Het belang van de sloop van de schuren is daarmee aangetoond. De inrichting en de werkwijze zijn van dien aard dat verstoring zo veel mogelijk wordt voorkomen. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen schuur</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</licensed>
		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>1</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</actuallyTaken>
		<populationSize>
			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het planten van de hoogstamfruitbomen en de inrichting en het beheer van het terrein dienen plaats te vinden zoals beschreven op pagina 5 en 6 van het bij de aanvraag gevoegde rapport ‘Ontheffingsaanvraag Flora- en faunawet sloop schuren Lendebosch te Hummelo’ van 18 augustus 2008.
8. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de soort waarvoor ontheffing is verleend, om verstoring in de meest kwetsbare perioden (voortplanting, winterrust) te voorkomen. De voortplantingsperiode van de steenuil loopt globaal van eind maart tot en met augustus. Afhankelijk van het seizoen en de weersomstandigheden kunnen deze perioden langer of korter zijn. De geschiktheid van de periode voor het uitvoeren van de werkzaamheden dient te worden bepaald door een deskundige1 op het gebied van de steenuil.
9. Vóór de sloop van de schuren dienen twee voor steenuilen geschikte nestkasten op het terrein te worden gerealiseerd.
10. De sloopwerkzaamheden dienen net vóór de balts van de steenuil plaats te vinden, in de periode half februari tot en met half maart.
11. Alle bovenstaande werkzaamheden dienen te worden uitgevoerd onder begeleiding van een ter zake kundige1 op het gebied van de steenuil.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Steenuil" in de gemeente Bronckhorst. Het betreft het gebied aan de Lendebosch 3 te Hummelo]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-11-24</licenseValidFrom>
		<licenseValidUntil>2009-03-15</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Picus viridis, Dendrocopos major, Dendrocopos minor]]></species>
		<regions>
			<region code="NL31">Utrecht</region>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[De voorgenomen velling van de laanbomen in het landgoed wordt door u gemotiveerd vanuit overwegingen van veiligheid, cultuurhistorie en ecologie. De vitaliteit van de laanbomen is afgenomen met als gevolg dat er regelmatig grote takken en stamdelen afbreken.
Dit gebeurt volgens u niet alleen tijdens het stormseizoen maar ook tijdens rustiger weer. Daarom leveren de bomen een gevaar op voor de gebruikers van het terrein. De ingreep is locatiegebonden. Er zijn vier alternatieven voor de werkwijze in overweging genomen:
1. De bomen niet vellen en op natuurlijke wijze laten aftakelen, waarbij ze zodanig worden behandeld dat ze geen gevaar opleveren. De bomen zijn echter zo groot dat niet te voorspellen is waar of wanneer takken of stamdelen gaan afbreken. Het gevaar is dan ook niet af te wenden.
2. De bomen kandelaberen. Dit zal het gevaar verminderen, maar belemmert het aanslaan van de nieuwe beplanting en biedt daarmee geen uitkomst voor het cultuurhistorische motief, namelijk het herstel van de lanen.
3. Drie bomen met holten kandelaberen en de overige vellen. Dit is zowel vanuit veiligheidsoverwegingen als cultuurhistorisch perspectief aanvaardbaar. Er zal een aantal potentiële verblijfplaatsen voor vleermuizen en vogels behouden blijven.
4. Alle bomen vellen. Dit is vanuit veiligheidsoverwegingen als cultuurhistorisch perspectief het meest wenselijk. Vanuit de zorgplicht van de Flora- en faunawet is deze optie echter niet reëel.
De bovengenoemde optie 1 is vanuit ecologisch oogpunt de meest wenselijke; deze wordt echter door u als onveilig beoordeeld. Gezien het omliggende bos, waarin naar verwachting geschikte holten aanwezig zijn voor vleermuizen, is het verdwijnen van een deel van de laanbomen acceptabel. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestbomen</method>
		</methods>
		<reasons>
			<reason code="FT">dwingende redenen van groot openbaar belang, met inbegrip van redenen van sociale of economische aard en voor het milieu wezenlijk gunstige effecten en de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
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		<actuallyTaken>
			<individuals>0</individuals>
			<eggs>0</eggs>
			<nests>3</nests>
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			<individuals>0</individuals>
			<breedingPairs>0</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de groene specht, grote bonte specht en de kleine bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de werkzaamheden dient rekening te worden gehouden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (broedseizoen, paartijd, winterrust) te voorkomen. De paar- en overwinteringsperiode van de ruige dwergvleermuis lopen globaal van half augustus tot en met half oktober, respectievelijk van half oktober tot en met half maart. Het broedseizoen van de groene specht, grote bonte specht en kleine bonte specht loopt globaal van half april tot en met eind juli. Afhankelijk van het seizoen en de weersomstandigheden kunnen deze perioden langer dan wel korter zijn. De geschiktheid van de periode voor het uitvoeren van de werkzaamheden dient te worden bepaald door (een) deskundige(n)1 op het gebied van vleermuizen en spechten.
10. Na het vellen en uitsnoeien van de bomen dienen de stammen van omgezaagde bomen tenminste één nacht met de holten naar boven gericht blijven liggen, voordat ze verwerkt worden.
12. Alle bovenstaande mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een deskundige1 op het gebied van de soorten waarvoor ontheffing wordt aangevraagd.
13. Bovenstaande mitigerende maatregelen dienen in een ecologisch werkprotocol te worden opgenomen. Dit ecologisch werkprotocol dient op de locatie aanwezig te zijn en onder betrokken werknemers bekend te zijn. Werkzaamheden dienen conform dit protocol te worden uitgevoerd.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Lanen landgoed Leeuwenburgh”, gelegen in gemeente Utrechtse Heuvelrug aan de Langbroekerdijk 39 en betreft 2 bomenlanen, (middenwestelijke laan) en (middenoostelijke laan)]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2009-01-01</licenseValidFrom>
		<licenseValidUntil>2013-03-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Athene noctua]]></species>
		<regions>
			<region code="NL42">Limburg (NL)</region>
		</regions>
		<alternativesAssessed><![CDATA[Om aan de milieu- en huisvestingsnormen in zake de varkenshouderij te kunnen voldoen is het noodzakelijk om enkele bestaande stallen af te breken en te vervangen door nieuwbouw. Er gaat ongeveer 0,4 hectare foerageergebied verloren in het plangebied, maar 0,5 hectare zal in het plangebied worden gecompenseerd. Onderzochte alternatieven zijn: Huidige situatie handhaven (niks doen), huidige situatie aanpassen, maar niet uitbreiden in stalruimte, bedrijf in zijn geheel verplaatsen. Als het bedrijf doorgaat zoals het nu is ingericht zal er een conflict ontstaan met andere wetgeving zoals het Besluit Huisvesting, waardoor deze varkenshouderij met de huidige milieuvergunning in de nabije toekomst niet meer zal voldoen aan de wet- en regelgeving en het bedrijf op termijn zal moeten sluiten. Ook dan zal het bedrijf uiteindelijk gesloopt worden met dezelfde gevolgen als de huidige sloop. Om te kunnen voldoen aan de wetgeving zullen de stallen aangepast moeten worden. De huidige traditionele stallen kunnen vanwege de bouwstaat en milieu- en huisvestingsnormen deels niet aangepast worden en zullen daarom deels opnieuw opgebouwd moeten worden. Door deze aanpassingen op de huidige oppervlakte te realiseren kunnen er minder dieren gehouden worden dan waar momenteel vergunning
voor verleend is.
Hierdoor kan het bedrijf niet rendabel draaiend worden gehouden en zal mogelijk het bedrijf gesloten moeten worden of een andere bedrijfstak op moeten zetten. Als het bedrijf in zijn geheel verplaatst wordt naar een nieuwe locatie zullen de bestaande stallen naar verwachting ter compensatie afgebroken dienen te worden. Dit heeft als negatief effect dat de verblijfmogelijkheden voor de steenuil in zijn geheel verdwijnen. Omdat huidige voortzetting niet mogelijk is, er voldoende maatregelen worden genomen om het verlies aan verblijfplaatsen te compenseren en er ook compensatie wordt geboden voor het verloren gaan van foerageergebied, komt de gunstige staat van instandhouding niet in gevaar. Het project, waarvoor ontheffing wordt aangevraagd, is probleemoplossend. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">slopen schuren en gebouwen, aantasting foerageergebied</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
			<individuals>0</individuals>
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			<otherNumber>0</otherNumber>
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			<individuals>0</individuals>
			<eggs>0</eggs>
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		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de steenuil komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. De sloop- en grondwerkzaamheden dienen buiten de voortplantingsperiode (april-half september) van de steenuil te worden uitgevoerd.
8. Eén week vóór aanvang van de sloop van de stal dienen, na het uitvliegen van de steenuilen, de dakplaten handmatig verwijderd te worden zodat de vaste rust- en verblijfplaats ongeschikt wordt gemaakt. Pas als is vastgesteld dat er geen steenuilen meer aanwezig zijn in de te slopen schuur kan begonnen worden met de sloopwerkzaamheden.
9. De dakbedekking dient handmatig te worden verwijderd en de sloop wordt in fases uitgevoerd.
10. De bouwwerkzaamheden dienen voornamelijk overdag te worden uitgevoerd. Gedurende de nacht dient geen verstoring op te treden in de vorm van verlichting en geluid.
11. De compensatie dient uitgevoerd te worden zoals beschreven in het bij de aanvraag gevoegde compensatieplan, geleverd bij de aanvullende informatie van 30 september 2008 en dient vóór aanvang van de werkzaamheden gereed te zijn.
12. Ter compensatie voor het verlies aan foerageergebied dient het meest oostelijke terreindeel en het westelijke terreindeel te worden ingericht ten behoeve van de steenuil.
13. Voorafgaande aan de sloopwerkzaamheden en de broedperiode dienen er buiten de verstorende invloed van de werkzaamheden meerdere alternatieve verblijf- en rustplaatsen aangeboden te worden in de vorm van steenuilnestkasten.
14. Minimaal twee weken vóór aanvang van de sloopwerkzaamheden dienen de steenuilenkasten geplaatst te worden, de locatie dient aan de volgende eisen te voldoen:
o De nestkast dient te worden geplaatst in of nabij een boom die voldoende dekking en schaduw geeft.
o De invliegopening van de nestkast dient goed bereikbaar te zijn voor de uil.
o De nestkast dient zo ver mogelijk verwijderd van de werkzaamheden geplaatst te worden.
o De nestkast dient niet boven of vlakbij het water geplaatst te worden.
o De nestkast dient 2 tot 4 meter boven het maaiveld te worden geplaatst.
15. De nestkasten dienen aan de zuidzijde en de zuidoostzijde van de stallen te worden opgehangen met een open verbinding naar geschikte jachthabitat.
16. Op het zuidoostelijke terrein dient een nestkast te worden geplaatst op een houten paal langs de zuidgrens van de locatie, omdat de te planten bomen te jong zijn om een zware nestkast te dragen.
17. De ter compensatie te plaatsen nestkasten dienen op voldoende afstand van de werkzaamheden te worden geplaatst om als alternatief verblijf te fungeren voor de steenuil.
18. Het exact vaststellen van de meest geschikte plekken dient ter plekke en op advies van een deskundige1 plaats te vinden.
19. Zoveel mogelijk bomen dienen gehandhaafd te blijven bij de herinrichting.
20. De verlichting van de nieuwe stal dient te worden aangepast op steenuilen.
21. Alle mitigerende en compenserende maatregelen dienen te worden uitgevoerd onder begeleiding van een deskundige1 op het gebied van steenuilen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project " Varkenshouderij van Heugten" gelegen aan de Bloemerstraat 15a in de gemeente Nederweert]]></location>
		<licensedJustification></licensedJustification>
	</derogation>
	<derogation directive="http://rod.eionet.europa.eu/obligations/276" user_derogation_ref="FF/75C/2008/0470" userIdentity="Alterra1" derogation_reference="Alterra1-B-111-2010022823272166">
		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
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		<licenseValidUntil>2013-12-31</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Dendrocopos major]]></species>
		<regions>
			<region code="NL22">Gelderland</region>
		</regions>
		<alternativesAssessed><![CDATA[Bij de planvorming is erkend dat de bestaande natuurwaarden in het geding zijn. In het masterplan van de gemeente Arnhem is het planologisch kader gegeven, waarbinnen ntwikkeling moet plaatsvinden. Het structuurbeeld geeft richting aan de ruimtelijke inkadering, de diverse deelgebieden en de ontsluiting. Voor de planopzet heeft een inventarisatie van de bestaande natuurwaarden plaatsgevonden. De rapportage heeft mede ten grondslag gelegen aan de betreffende onderdelen van het masterplan en als zodanig aan de uitgangspunten voor de ontwikkelingsvisie toegevoegd. Het is niet duidelijk of er andere locaties voorhanden zijn, die minder negatieve effecten hebben op de aanwezige beschermde soorten. Echter, de meeste ruimtelijke ingrepen vinden plaats op sportvelden en open plekken, waardoor de verstorende effecten beperkt blijven.
Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">nestbomen kappen</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezende uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling.</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
		<licensed>
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			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de  grote bonte specht komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de werkzaamheden dient rekening te worden gehouden met de seizoensactiviteiten van de soorten waarvoor ontheffing wordt verleend, om verstoring in de meest kwetsbare perioden (voortplanting) te voorkomen. De voortplantingsperiode van de grote bonte specht loopt globaal van maart tot en met juli. Afhankelijk van het seizoen en de weersomstandigheden kunnen deze perioden langer dan wel korter zijn. De geschiktheid van de periode voor het uitvoeren van de werkzaamheden dient te worden bepaald door een deskundige1 op het gebied van broedvogels.
8. Voorafgaand aan de verstorende werkzaamheden dienen exemplaren van de wilde marjolein verplaatst te worden naar een geschikte groeiplek in de directe omgeving van het plangebied. Een deskundige1 op het gebied van planten dient dit te begeleiden.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Herontwikkeling voormalig kazerneterrein Saksen Weimar" in de gemeente Arnhem begrensd door de Apeldoornseweg aan de westzijde, de Monnikensteeg aan de oostzijde en de Weg achter het Bos aan de zuidzijde]]></location>
		<licensedJustification></licensedJustification>
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		<licensingAuthority><![CDATA[DE MINISTER VAN LANDBOUW, NATUUR EN VOEDSELKWALITEIT]]></licensingAuthority>
		<licenseValidFrom>2008-12-12</licenseValidFrom>
		<licenseValidUntil>2012-11-01</licenseValidUntil>
		<numberOfLicenses><![CDATA[1]]></numberOfLicenses>
		<species><![CDATA[Accipiter gentilus]]></species>
		<regions>
			<region code="NL32">Noord-Holland</region>
		</regions>
		<alternativesAssessed><![CDATA[De effecten van de werkzaamheden op de aanwezige beschermde soorten zijn niet meegenomen in de uitgevoerde alternatievenafweging. De alternatieven zijn ten aanzien van de beschermde soorten niet beter of slechter dan het gekozen uitvoeringsalternatief. Het niet-uitvoeren van de saneringswerkzaamheden is gezien de sterke mate van verontreiniging geen alternatief. Door het uitvoeren van mitigerende maatregelen wordt er zorgvuldig gehandeld en komt de gunstige staat van instandhouding van de beschermde soorten niet in het geding door de voorgenomen werkzaamheden. Hiermee is het voldoende aangetoond dat geen andere bevredigende oplossing voorhanden is.]]></alternativesAssessed>
		<activities>
		</activities>
		<methods>
			<method code="FT">kappen nestboom</method>
		</methods>
		<reasons>
			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
		</reasons>
		<strictlySupervisedConditions></strictlySupervisedConditions>
		<selectiveBasis></selectiveBasis>
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			<individuals>0</individuals>
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			<individuals>0</individuals>
			<breedingPairs>1</breedingPairs>
			<otherType></otherType>
			<otherNumber>0</otherNumber>
		</populationSize>
		<impactOnPopulation><![CDATA[De gunstige staat van instandhouding van de havik komt niet in gevaar]]></impactOnPopulation>
		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de havik, om verstoring in de meest kwetsbare periode (voortplanting) te voorkomen. Kapwerkzaamheden en overige werkzaamheden die verstoring van broedgevallen van de havik veroorzaken, dienen buiten de broedperiode van de havik uitgevoerd te worden.
8. Een deskundige1 op het gebied van vogels dient te bepalen of er sprake is van een broedgeval van de havik. Tevens dient deze persoon te bepalen wanneer de verstorende werkzaamheden uitgevoerd kunnen worden.
9. Aangetroffen exemplaren van de bittervoorn dienen weggevangen en verplaatst te worden naar geschikt biotoop in de directe omgeving van het plangebied, maar buiten de invloedszone van de werkzaamheden.
10. Alle bovenstaande mitigerende maatregelen dienen te worden uitgevoerd onder begeleiding van een deskundige1 op het gebied van de soorten waarvoor ontheffing is verleend.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[project "Sanering Slochtereiland" in de gemeente Amsterdam, gelegen ten noordoosten van Amsterdam, tussen Landsmeer en Zunderdorp, in het Noordhollandsch Kanaal, ten westen van de N247 van Amsterdam richting Purmerend]]></location>
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			<method code="FT">slopen gebouw</method>
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			<reason code="FT">onder andere aangewezen de uitvoering van werkzaamheden in het kader van ruimtelijke inrichting of ontwikkeling</reason>
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		<supervisoryMeasure><![CDATA[Specifieke voorwaarden
7. Het compensatiegebied voor de steenuil rondom de nieuwe ontsluitingsweg dient aangelegd te worden conform punt 3 van de bij de aanvraag aangeleverde bijlage 4 ‘Toelichting op de ontheffingsaanvraag uitbreiding bedrijventerrein stadhoudersmolen, gemeente Apeldoorn (projectbeschrijving) en conform de bij de aanvraag gevoegde kaart ‘Definitief inrichtingsplan omgeving ontsluitingsweg Stadhoudersmolen’ van augustus 2008 (bijlage 5), met dien verstande dat in de bloemrijke graslanden en onder de boomgaard minimaal twee maal per jaar gemaaid dient te worden of begrazing dient te worden ingezet.
8. Aanvullend op deze compenserende maatregelen dienen in de wegbermen van de ontsluitingsweg geen paaltjes of solitaire bomen geplaatst te worden. Daarnaast dienen er in het compensatiegebied minimaal 3 nestkasten opgehangen te worden.
9. Een deskundige1 op het gebied van de steenuil dient betrokken te worden bij de inrichting van het compensatiegebied, zodat geschikt foerageergebied ontstaat, goede nestkastlocaties worden gekozen en verkeersslachtoffers onder de steenuil voorkomen worden.
10. Het compensatiegebied dient voor 2010 ingericht te zijn.
11. Bij de planning van de werkzaamheden dient rekening gehouden te worden met de seizoensactiviteiten van de steenuil, om verstoring in de meest kwetsbare periode (voortplanting) te voorkomen. De voortplantingsperiode van de steenuil loopt globaal van januari tot en met augustus. Afhankelijk van het seizoen en de weersomstandigheden kan deze periode langer dan wel korter zijn.
12. De vaste rust- en verblijfplaats van de steenuil dient verwijderd te worden in de periode augustus-januari door een deskundige op het gebied van steenuilen.]]></supervisoryMeasure>
		<sensitive>false</sensitive>
		<comments><![CDATA[1 Met een deskundige wordt bedoeld een persoon die voor de situatie en soorten ten aanzien waarvan hij of zij gevraagd is te adviseren en/of te begeleiden, aantoonbare ervaring en kennis heeft op het gebied van soortspecifieke ecologie. De ervaring en kennis dient te zijn opgedaan doordat de deskundige:
- op HBO-, dan wel universitair niveau een opleiding heeft genoten met als zwaartepunt (Nederlandse) ecologie; en/of
- als ecoloog werkzaam is voor een ecologisch adviesbureau; en/of
- zich aantoonbaar actief inzet op het gebied van de soortenbescherming en is aangesloten bij en werkzaam voor de daarvoor in Nederland bestaande organisaties (zoals bijvoorbeeld Zoogdiervereniging VZZ, RAVON, Vogelbescherming Nederland, Vlinderstichting, Natuurhistorisch Genootschap, KNNV, NJN, IVN, EIS Nederland, FLORON, SOVON, STONE, Staatsbosbeheer, Natuurmonumenten, De Landschappen en Stichting Beheer Natuur en Landelijk gebied) en/of
- zich aantoonbaar actief inzet op het gebied van de soortenmonitoring en/of - bescherming.]]></comments>
		<location><![CDATA[het project "Uitbreiding bedrijventerrein Stadhoudermolen" in de gemeente Apeldoorn. Het betreft grasland ten noorden van Apeldoorn,]]></location>
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