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<dc:title xml:lang="en"><![CDATA[Wpływ gospodarki leśnej na rozmieszczenie dzięcioła trójpalczastego w Puszczy Białowieskiej: konsekwencje dla ochrony gatunku]]></dc:title>
<dc:title xml:lang="en"><![CDATA[Effects of forest management on Three-toed Woodpecker]]></dc:title>
<dc:title xml:lang="en"><![CDATA[Effects of Forest Management on Three-toed Woodpecker Picoides tridactylus Distribution in the Białowieża Forest (NE Poland): Conservation Implications]]></dc:title>
<dc:title xml:lang="pl"><![CDATA[Wpływ gospodarki leśnej na rozmieszczenie dzięcioła trójpalczastego w Puszczy Białowieskiej: konsekwencje dla ochrony gatunku]]></dc:title>
<dc:title xml:lang="pl"><![CDATA[Effects of forest management on Three-toed Woodpecker]]></dc:title>
<dc:title xml:lang="pl"><![CDATA[Effects of Forest Management on Three-toed Woodpecker Picoides tridactylus Distribution in the Białowieża Forest (NE Poland): Conservation Implications]]></dc:title>
<dc:creator><![CDATA[Wesołwski, Tomasz]]></dc:creator>
<dc:creator><![CDATA[Czeszczewik, Dorota]]></dc:creator>
<dc:creator><![CDATA[Rowiński, Patryk]]></dc:creator>
<dc:subject xml:lang="en"><![CDATA[Three-toed Woodpecker]]></dc:subject>
<dc:subject xml:lang="en"><![CDATA[Picoides tridactylus]]></dc:subject>
<dc:subject xml:lang="en"><![CDATA[conservation of endangered species]]></dc:subject>
<dc:subject xml:lang="en"><![CDATA[primeval forest]]></dc:subject>
<dc:subject xml:lang="en"><![CDATA[dead wood]]></dc:subject>
<dc:subject xml:lang="en"><![CDATA[snags]]></dc:subject>
<dc:subject xml:lang="en"><![CDATA[dzięcioł trójpalczasty]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[Three-toed Woodpecker]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[Picoides tridactylus]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[conservation of endangered species]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[primeval forest]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[dead wood]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[snags]]></dc:subject>
<dc:subject xml:lang="pl"><![CDATA[dzięcioł trójpalczasty]]></dc:subject>
<dc:description xml:lang="en"><![CDATA[pg(s) 53–60]]></dc:description>
<dc:description xml:lang="en"><![CDATA[Distribution of Three-toed Woodpeckers and that of dead wood were mapped in two fragments of the Białowieża National Park (BNP) differing in their management history — primeval (old-growth stands of natural origin, no human intervention) and logged (as the former but subject to 80 years of commercial forestry). Data were collected during the breeding seasons 1999–2001. In the end of April 2000, the whole BNP was systematically searched; playbacks of drumming were used to enhance detection of birds. Presence/absence of Three-toed Woodpeckers and of dead wood (standing and downed Norway spruces and snags of other trees) were recorded within each forest sub-compartments (ca. 28 ha). Data from censuses done in smaller plots in 1975–1999 showed that in the primeval forest the woodpeckers bred twice more frequently in swampy and coniferous forests than in the oak-hornbeam habitat. These preferred habitat types covered larger areas in the logged fragment than in the primeval part (66% vs. 41%). Yet despite this, Three-toed Woodpeckers were recorded there over twice less frequently (14% of 176 sub-compartments) than in the primeval (36% of 164 sub-compartments) part. These differences followed sharp contrasts in the dead wood availability; all but one sub-compartments in the primeval fragment contained some form of dead wood, whereas dead spruces were missing in almost 30% of sub-compartments in the logged part. This was the effect of continuous “sanitary” logging, purposeful removal of dying and dead spruces from the Forest. To restore Three-toed Woodpecker habitats it is necessary to ban removal of dead spruces in the managed part of BNP. However, the BNP area is too small, to assure the long-term survival of the Białowieża Forest population. To achieve this, it is necessary to resign from removal of dying and dead spruces in the whole Polish part of the Białowieża Forest (600 km2). This would create breeding habitat for a maximum 260–320 pairs.]]></dc:description>
<dc:description xml:lang="pl"><![CDATA[pg(s) 53–60]]></dc:description>
<dc:description xml:lang="pl"><![CDATA[Distribution of Three-toed Woodpeckers and that of dead wood were mapped in two fragments of the Białowieża National Park (BNP) differing in their management history — primeval (old-growth stands of natural origin, no human intervention) and logged (as the former but subject to 80 years of commercial forestry). Data were collected during the breeding seasons 1999–2001. In the end of April 2000, the whole BNP was systematically searched; playbacks of drumming were used to enhance detection of birds. Presence/absence of Three-toed Woodpeckers and of dead wood (standing and downed Norway spruces and snags of other trees) were recorded within each forest sub-compartments (ca. 28 ha). Data from censuses done in smaller plots in 1975–1999 showed that in the primeval forest the woodpeckers bred twice more frequently in swampy and coniferous forests than in the oak-hornbeam habitat. These preferred habitat types covered larger areas in the logged fragment than in the primeval part (66% vs. 41%). Yet despite this, Three-toed Woodpeckers were recorded there over twice less frequently (14% of 176 sub-compartments) than in the primeval (36% of 164 sub-compartments) part. These differences followed sharp contrasts in the dead wood availability; all but one sub-compartments in the primeval fragment contained some form of dead wood, whereas dead spruces were missing in almost 30% of sub-compartments in the logged part. This was the effect of continuous “sanitary” logging, purposeful removal of dying and dead spruces from the Forest. To restore Three-toed Woodpecker habitats it is necessary to ban removal of dead spruces in the managed part of BNP. However, the BNP area is too small, to assure the long-term survival of the Białowieża Forest population. To achieve this, it is necessary to resign from removal of dying and dead spruces in the whole Polish part of the Białowieża Forest (600 km2). This would create breeding habitat for a maximum 260–320 pairs.]]></dc:description>
<dc:publisher><![CDATA[Museum and Institute of Zoology, Polish Academy of Sciences]]></dc:publisher>
<dc:contributor><![CDATA[Museum and Institute of Zoology, Polish Academy of Sciences]]></dc:contributor>
<dc:date><![CDATA[2005]]></dc:date>
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<dc:identifier><![CDATA[10.3161/068.040.0111]]></dc:identifier>
<dc:identifier><![CDATA[https://rcin.org.pl/miiz/dlibra/publication/75762/edition/55532/content]]></dc:identifier>
<dc:identifier><![CDATA[oai:rcin.org.pl:55532]]></dc:identifier>
<dc:source xml:lang="en"><![CDATA[MiIZ PAN, call no. P.257]]></dc:source>
<dc:source xml:lang="en"><![CDATA[MiIZ PAN, call no. P.4568]]></dc:source>
<dc:source xml:lang="pl"><![CDATA[MiIZ PAN, sygn. P.257]]></dc:source>
<dc:source xml:lang="pl"><![CDATA[MiIZ PAN, sygn. P.4568]]></dc:source>
<dc:language><![CDATA[eng]]></dc:language>
<dc:relation><![CDATA[Acta Ornithologica]]></dc:relation>
<dc:relation><![CDATA[oai:rcin.org.pl:publication:75762]]></dc:relation>
<dc:rights xml:lang="en"><![CDATA[Rights Reserved - Free Access]]></dc:rights>
<dc:rights xml:lang="pl"><![CDATA[Prawa zastrzeżone - dostęp nieograniczony]]></dc:rights>
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