Demographic models and reserve designs for the California spotted owl
The California Spotted Owl (Strix occidentalis occidentalis), like the more well-known Northern Spotted Owl (Strix occidentalis caurina), appears to be in decline over at least a part of its geographic range. Two different types of reserve design have been implemented to protect Spotted Owls. The Sp...
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Veröffentlicht in: | Ecological applications 1995-08, Vol.5 (3), p.639-647 |
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description | The California Spotted Owl (Strix occidentalis occidentalis), like the more well-known Northern Spotted Owl (Strix occidentalis caurina), appears to be in decline over at least a part of its geographic range. Two different types of reserve design have been implemented to protect Spotted Owls. The Spotted Owl Habitat Area (SOHA) system uses a fairly large number of small reserves; each SOHA is capable of supporting 1-3 nesting owl pairs. The Habitat Conservation Area (HCA) plan proposes a smaller number of fairly large reserves, each including 10-20 active Spotted Owl nests. The HCA reserve design strategy has been incorporated into current conservation planning for the Northern Spotted Owl. The Technical Assessment Team of the California Spotted Owl Assessment project has recommended preserving existing SOHAs within a lightly harvested matrix as an interim policy for conservation of the California Spotted Owl. In this paper we present results from two demographic models of the California Spotted Owl. The first model is based on a simple formulation of a birth--death process; the second model is a somewhat more detailed simulation model. The models are intended to provide a comparison of the SOHA and HCA reserve-design strategies. We are particularly interested in the ability of the two reserve designs to withstand recurring environmental catastrophes in the form of forest fires. The HCA strategy always leads to longer persistence times than the SOHA strategy. The essential difference between the two strategies appears to lie in the shape of the function that gives the probability of colonization of an empty nest site. These results have several implications for the conservation of California Spotted Owls and for conservation biology in general. (1) Some variant of the HCA reserve design strategy may be preferable to the interim strategy being proposed for conservation of the California Spotted Owl. (2) Simple, parameter-sparse models like ours can yield results comparable to those of more complex and detailed models. (3) Models that include the effects of catastrophic environmental perturbations have great potential for application in conservation biology. |
doi_str_mv | 10.2307/1941973 |
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Two different types of reserve design have been implemented to protect Spotted Owls. The Spotted Owl Habitat Area (SOHA) system uses a fairly large number of small reserves; each SOHA is capable of supporting 1-3 nesting owl pairs. The Habitat Conservation Area (HCA) plan proposes a smaller number of fairly large reserves, each including 10-20 active Spotted Owl nests. The HCA reserve design strategy has been incorporated into current conservation planning for the Northern Spotted Owl. The Technical Assessment Team of the California Spotted Owl Assessment project has recommended preserving existing SOHAs within a lightly harvested matrix as an interim policy for conservation of the California Spotted Owl. In this paper we present results from two demographic models of the California Spotted Owl. The first model is based on a simple formulation of a birth--death process; the second model is a somewhat more detailed simulation model. The models are intended to provide a comparison of the SOHA and HCA reserve-design strategies. We are particularly interested in the ability of the two reserve designs to withstand recurring environmental catastrophes in the form of forest fires. The HCA strategy always leads to longer persistence times than the SOHA strategy. The essential difference between the two strategies appears to lie in the shape of the function that gives the probability of colonization of an empty nest site. These results have several implications for the conservation of California Spotted Owls and for conservation biology in general. (1) Some variant of the HCA reserve design strategy may be preferable to the interim strategy being proposed for conservation of the California Spotted Owl. (2) Simple, parameter-sparse models like ours can yield results comparable to those of more complex and detailed models. (3) Models that include the effects of catastrophic environmental perturbations have great potential for application in conservation biology.</description><identifier>ISSN: 1051-0761</identifier><identifier>EISSN: 1939-5582</identifier><identifier>DOI: 10.2307/1941973</identifier><language>eng</language><publisher>The Ecological Society of America</publisher><subject>CALIFORNIA ; CALIFORNIE ; CONCEPTION ; CONSERVACION DE LA NATURALEZA ; Conservation biology ; CONSERVATION DE LA NATURE ; DEMOGRAFIA ; DEMOGRAPHIE ; DEMOGRAPHY ; DESIGN ; DINAMICA DE LA POBLACION ; DISENO ; DYNAMIQUE DES POPULATIONS ; ECOLOGIA ; ECOLOGIE ; ECOLOGY ; ENDANGERED SPECIES ; ENVIRONMENTAL PROTECTION ; ESPECE EN DANGER ; ESPECIES EN PELIGRO DE EXTINCION ; FAUNE ET FLORE SAUVAGES ; Forest conservation ; Forest habitats ; Habitat conservation ; habitat conservation area ; MATHEMATICAL MODELS ; Metapopulation ecology ; MODELE DE SIMULATION ; MODELE MATHEMATIQUE ; Modeling ; MODELOS DE SIMULACION ; MODELOS MATEMATICOS ; NATURE CONSERVATION ; NATURE RESERVES ; Nesting sites ; Owls ; Parametric models ; POPULATION DYNAMICS ; POPULATION ECOLOGY ; PROTECCION AMBIENTAL ; PROTECTION DE L'ENVIRONNEMENT ; RESERVAS NATURALES ; RESERVE NATURELLE ; SIMULATION MODELS ; Simulations ; spotted owl habitat area ; STRIGIFORMES ; STRIX OCCIDENTALIS ; Strix occidentalis occidentalis ; VIDA SILVESTRE ; WILDLIFE</subject><ispartof>Ecological applications, 1995-08, Vol.5 (3), p.639-647</ispartof><rights>Copyright 1995 The Ecological Society of America</rights><rights>1995 by the Ecological Society of America</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c3449-66e8fb0c5572a407a8ee41c9732ef178a8fd937c936ab7fe6c72f3c551e142d33</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/1941973$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/1941973$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>315,781,785,804,27929,27930,58022,58255</link.rule.ids></links><search><creatorcontrib>Andersen, Mark C.</creatorcontrib><creatorcontrib>Mahato, Dipak</creatorcontrib><title>Demographic models and reserve designs for the California spotted owl</title><title>Ecological applications</title><description>The California Spotted Owl (Strix occidentalis occidentalis), like the more well-known Northern Spotted Owl (Strix occidentalis caurina), appears to be in decline over at least a part of its geographic range. Two different types of reserve design have been implemented to protect Spotted Owls. The Spotted Owl Habitat Area (SOHA) system uses a fairly large number of small reserves; each SOHA is capable of supporting 1-3 nesting owl pairs. The Habitat Conservation Area (HCA) plan proposes a smaller number of fairly large reserves, each including 10-20 active Spotted Owl nests. The HCA reserve design strategy has been incorporated into current conservation planning for the Northern Spotted Owl. The Technical Assessment Team of the California Spotted Owl Assessment project has recommended preserving existing SOHAs within a lightly harvested matrix as an interim policy for conservation of the California Spotted Owl. In this paper we present results from two demographic models of the California Spotted Owl. The first model is based on a simple formulation of a birth--death process; the second model is a somewhat more detailed simulation model. The models are intended to provide a comparison of the SOHA and HCA reserve-design strategies. We are particularly interested in the ability of the two reserve designs to withstand recurring environmental catastrophes in the form of forest fires. The HCA strategy always leads to longer persistence times than the SOHA strategy. The essential difference between the two strategies appears to lie in the shape of the function that gives the probability of colonization of an empty nest site. These results have several implications for the conservation of California Spotted Owls and for conservation biology in general. (1) Some variant of the HCA reserve design strategy may be preferable to the interim strategy being proposed for conservation of the California Spotted Owl. (2) Simple, parameter-sparse models like ours can yield results comparable to those of more complex and detailed models. (3) Models that include the effects of catastrophic environmental perturbations have great potential for application in conservation biology.</description><subject>CALIFORNIA</subject><subject>CALIFORNIE</subject><subject>CONCEPTION</subject><subject>CONSERVACION DE LA NATURALEZA</subject><subject>Conservation biology</subject><subject>CONSERVATION DE LA NATURE</subject><subject>DEMOGRAFIA</subject><subject>DEMOGRAPHIE</subject><subject>DEMOGRAPHY</subject><subject>DESIGN</subject><subject>DINAMICA DE LA POBLACION</subject><subject>DISENO</subject><subject>DYNAMIQUE DES POPULATIONS</subject><subject>ECOLOGIA</subject><subject>ECOLOGIE</subject><subject>ECOLOGY</subject><subject>ENDANGERED SPECIES</subject><subject>ENVIRONMENTAL PROTECTION</subject><subject>ESPECE EN DANGER</subject><subject>ESPECIES EN PELIGRO DE EXTINCION</subject><subject>FAUNE ET FLORE SAUVAGES</subject><subject>Forest conservation</subject><subject>Forest habitats</subject><subject>Habitat conservation</subject><subject>habitat conservation area</subject><subject>MATHEMATICAL MODELS</subject><subject>Metapopulation ecology</subject><subject>MODELE DE SIMULATION</subject><subject>MODELE MATHEMATIQUE</subject><subject>Modeling</subject><subject>MODELOS DE SIMULACION</subject><subject>MODELOS MATEMATICOS</subject><subject>NATURE CONSERVATION</subject><subject>NATURE RESERVES</subject><subject>Nesting sites</subject><subject>Owls</subject><subject>Parametric models</subject><subject>POPULATION DYNAMICS</subject><subject>POPULATION ECOLOGY</subject><subject>PROTECCION AMBIENTAL</subject><subject>PROTECTION DE L'ENVIRONNEMENT</subject><subject>RESERVAS NATURALES</subject><subject>RESERVE NATURELLE</subject><subject>SIMULATION MODELS</subject><subject>Simulations</subject><subject>spotted owl habitat area</subject><subject>STRIGIFORMES</subject><subject>STRIX OCCIDENTALIS</subject><subject>Strix occidentalis occidentalis</subject><subject>VIDA SILVESTRE</subject><subject>WILDLIFE</subject><issn>1051-0761</issn><issn>1939-5582</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1995</creationdate><recordtype>article</recordtype><recordid>eNp9kD1PwzAQhiMEEqUgdiYPCKaAP2I7HqtSPqRKIEFny03ObaokDnZK1X-Pq3SFW-4dnnt1epLkmuAHyrB8JCojSrKTZEQUUynnOT2NGXOSYinIeXIRwgbHoZSOktkTNG7lTbeuCtS4EuqATFsiDwH8D6ASQrVqA7LOo34NaGrqKua2Mih0ru-hRG5XXyZn1tQBro57nCyeZ1_T13T-_vI2nczTgmWZSoWA3C5xwbmkJsPS5AAZKeK3FCyRucltqZgsFBNmKS2IQlLLIk6AZLRkbJzcDb2dd99bCL1uqlBAXZsW3DZoIvJMMawieD-AhXcheLC681Vj_F4TrA-a9FFTJMlA7qoa9n9hejb5IEpxzgQ7tN8ON5vQO_9P9c2AWeO0Wfkq6MWnEtG84uwX_wN63g</recordid><startdate>199508</startdate><enddate>199508</enddate><creator>Andersen, Mark C.</creator><creator>Mahato, Dipak</creator><general>The Ecological Society of America</general><general>Ecological Society of America</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>C1K</scope></search><sort><creationdate>199508</creationdate><title>Demographic models and reserve designs for the California spotted owl</title><author>Andersen, Mark C. ; Mahato, Dipak</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3449-66e8fb0c5572a407a8ee41c9732ef178a8fd937c936ab7fe6c72f3c551e142d33</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1995</creationdate><topic>CALIFORNIA</topic><topic>CALIFORNIE</topic><topic>CONCEPTION</topic><topic>CONSERVACION DE LA NATURALEZA</topic><topic>Conservation biology</topic><topic>CONSERVATION DE LA NATURE</topic><topic>DEMOGRAFIA</topic><topic>DEMOGRAPHIE</topic><topic>DEMOGRAPHY</topic><topic>DESIGN</topic><topic>DINAMICA DE LA POBLACION</topic><topic>DISENO</topic><topic>DYNAMIQUE DES POPULATIONS</topic><topic>ECOLOGIA</topic><topic>ECOLOGIE</topic><topic>ECOLOGY</topic><topic>ENDANGERED SPECIES</topic><topic>ENVIRONMENTAL PROTECTION</topic><topic>ESPECE EN DANGER</topic><topic>ESPECIES EN PELIGRO DE EXTINCION</topic><topic>FAUNE ET FLORE SAUVAGES</topic><topic>Forest conservation</topic><topic>Forest habitats</topic><topic>Habitat conservation</topic><topic>habitat conservation area</topic><topic>MATHEMATICAL MODELS</topic><topic>Metapopulation ecology</topic><topic>MODELE DE SIMULATION</topic><topic>MODELE MATHEMATIQUE</topic><topic>Modeling</topic><topic>MODELOS DE SIMULACION</topic><topic>MODELOS MATEMATICOS</topic><topic>NATURE CONSERVATION</topic><topic>NATURE RESERVES</topic><topic>Nesting sites</topic><topic>Owls</topic><topic>Parametric models</topic><topic>POPULATION DYNAMICS</topic><topic>POPULATION ECOLOGY</topic><topic>PROTECCION AMBIENTAL</topic><topic>PROTECTION DE L'ENVIRONNEMENT</topic><topic>RESERVAS NATURALES</topic><topic>RESERVE NATURELLE</topic><topic>SIMULATION MODELS</topic><topic>Simulations</topic><topic>spotted owl habitat area</topic><topic>STRIGIFORMES</topic><topic>STRIX OCCIDENTALIS</topic><topic>Strix occidentalis occidentalis</topic><topic>VIDA SILVESTRE</topic><topic>WILDLIFE</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Andersen, Mark C.</creatorcontrib><creatorcontrib>Mahato, Dipak</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><jtitle>Ecological applications</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Andersen, Mark C.</au><au>Mahato, Dipak</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Demographic models and reserve designs for the California spotted owl</atitle><jtitle>Ecological applications</jtitle><date>1995-08</date><risdate>1995</risdate><volume>5</volume><issue>3</issue><spage>639</spage><epage>647</epage><pages>639-647</pages><issn>1051-0761</issn><eissn>1939-5582</eissn><abstract>The California Spotted Owl (Strix occidentalis occidentalis), like the more well-known Northern Spotted Owl (Strix occidentalis caurina), appears to be in decline over at least a part of its geographic range. Two different types of reserve design have been implemented to protect Spotted Owls. The Spotted Owl Habitat Area (SOHA) system uses a fairly large number of small reserves; each SOHA is capable of supporting 1-3 nesting owl pairs. The Habitat Conservation Area (HCA) plan proposes a smaller number of fairly large reserves, each including 10-20 active Spotted Owl nests. The HCA reserve design strategy has been incorporated into current conservation planning for the Northern Spotted Owl. The Technical Assessment Team of the California Spotted Owl Assessment project has recommended preserving existing SOHAs within a lightly harvested matrix as an interim policy for conservation of the California Spotted Owl. In this paper we present results from two demographic models of the California Spotted Owl. The first model is based on a simple formulation of a birth--death process; the second model is a somewhat more detailed simulation model. The models are intended to provide a comparison of the SOHA and HCA reserve-design strategies. We are particularly interested in the ability of the two reserve designs to withstand recurring environmental catastrophes in the form of forest fires. The HCA strategy always leads to longer persistence times than the SOHA strategy. The essential difference between the two strategies appears to lie in the shape of the function that gives the probability of colonization of an empty nest site. These results have several implications for the conservation of California Spotted Owls and for conservation biology in general. (1) Some variant of the HCA reserve design strategy may be preferable to the interim strategy being proposed for conservation of the California Spotted Owl. (2) Simple, parameter-sparse models like ours can yield results comparable to those of more complex and detailed models. (3) Models that include the effects of catastrophic environmental perturbations have great potential for application in conservation biology.</abstract><pub>The Ecological Society of America</pub><doi>10.2307/1941973</doi><tpages>9</tpages></addata></record> |
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subjects | CALIFORNIA CALIFORNIE CONCEPTION CONSERVACION DE LA NATURALEZA Conservation biology CONSERVATION DE LA NATURE DEMOGRAFIA DEMOGRAPHIE DEMOGRAPHY DESIGN DINAMICA DE LA POBLACION DISENO DYNAMIQUE DES POPULATIONS ECOLOGIA ECOLOGIE ECOLOGY ENDANGERED SPECIES ENVIRONMENTAL PROTECTION ESPECE EN DANGER ESPECIES EN PELIGRO DE EXTINCION FAUNE ET FLORE SAUVAGES Forest conservation Forest habitats Habitat conservation habitat conservation area MATHEMATICAL MODELS Metapopulation ecology MODELE DE SIMULATION MODELE MATHEMATIQUE Modeling MODELOS DE SIMULACION MODELOS MATEMATICOS NATURE CONSERVATION NATURE RESERVES Nesting sites Owls Parametric models POPULATION DYNAMICS POPULATION ECOLOGY PROTECCION AMBIENTAL PROTECTION DE L'ENVIRONNEMENT RESERVAS NATURALES RESERVE NATURELLE SIMULATION MODELS Simulations spotted owl habitat area STRIGIFORMES STRIX OCCIDENTALIS Strix occidentalis occidentalis VIDA SILVESTRE WILDLIFE |
title | Demographic models and reserve designs for the California spotted owl |
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