Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico
Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes betwee...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
López-García, José [verfasserIn] Navarro-Cerrillo, Rafael M. [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2019 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Journal of forestry research - Harbin : Univ., 1990, 31(2019), 5 vom: 09. Mai, Seite 1551-1566 |
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| Übergeordnetes Werk: |
volume:31 ; year:2019 ; number:5 ; day:09 ; month:05 ; pages:1551-1566 |
| Links: |
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| DOI / URN: |
10.1007/s11676-019-00964-3 |
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| Katalog-ID: |
SPR040872882 |
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| 100 | 1 | |a López-García, José |e verfasserin |4 aut | |
| 245 | 1 | 0 | |a Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico |
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| 520 | |a Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. | ||
| 650 | 4 | |a Illegal logging |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Forest density change |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Forest recovery |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Conifer forests |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Monarch Butterfly Biosphere Reserve |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Navarro-Cerrillo, Rafael M. |e verfasserin |4 aut | |
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10.1007/s11676-019-00964-3 doi (DE-627)SPR040872882 (SPR)s11676-019-00964-3-e DE-627 ger DE-627 rakwb eng 630 640 ASE López-García, José verfasserin aut Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. Illegal logging (dpeaa)DE-He213 Forest density change (dpeaa)DE-He213 Forest recovery (dpeaa)DE-He213 Conifer forests (dpeaa)DE-He213 Monarch Butterfly Biosphere Reserve (dpeaa)DE-He213 Navarro-Cerrillo, Rafael M. verfasserin aut Enthalten in Journal of forestry research Harbin : Univ., 1990 31(2019), 5 vom: 09. Mai, Seite 1551-1566 (DE-627)529093545 (DE-600)2299615-1 1993-0607 nnns volume:31 year:2019 number:5 day:09 month:05 pages:1551-1566 https://dx.doi.org/10.1007/s11676-019-00964-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-FOR SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_121 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2036 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2700 GBV_ILN_2817 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4367 GBV_ILN_4392 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 AR 31 2019 5 09 05 1551-1566 |
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10.1007/s11676-019-00964-3 doi (DE-627)SPR040872882 (SPR)s11676-019-00964-3-e DE-627 ger DE-627 rakwb eng 630 640 ASE López-García, José verfasserin aut Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. Illegal logging (dpeaa)DE-He213 Forest density change (dpeaa)DE-He213 Forest recovery (dpeaa)DE-He213 Conifer forests (dpeaa)DE-He213 Monarch Butterfly Biosphere Reserve (dpeaa)DE-He213 Navarro-Cerrillo, Rafael M. verfasserin aut Enthalten in Journal of forestry research Harbin : Univ., 1990 31(2019), 5 vom: 09. Mai, Seite 1551-1566 (DE-627)529093545 (DE-600)2299615-1 1993-0607 nnns volume:31 year:2019 number:5 day:09 month:05 pages:1551-1566 https://dx.doi.org/10.1007/s11676-019-00964-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-FOR SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_121 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2036 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2700 GBV_ILN_2817 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4367 GBV_ILN_4392 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 AR 31 2019 5 09 05 1551-1566 |
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10.1007/s11676-019-00964-3 doi (DE-627)SPR040872882 (SPR)s11676-019-00964-3-e DE-627 ger DE-627 rakwb eng 630 640 ASE López-García, José verfasserin aut Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. Illegal logging (dpeaa)DE-He213 Forest density change (dpeaa)DE-He213 Forest recovery (dpeaa)DE-He213 Conifer forests (dpeaa)DE-He213 Monarch Butterfly Biosphere Reserve (dpeaa)DE-He213 Navarro-Cerrillo, Rafael M. verfasserin aut Enthalten in Journal of forestry research Harbin : Univ., 1990 31(2019), 5 vom: 09. Mai, Seite 1551-1566 (DE-627)529093545 (DE-600)2299615-1 1993-0607 nnns volume:31 year:2019 number:5 day:09 month:05 pages:1551-1566 https://dx.doi.org/10.1007/s11676-019-00964-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-FOR SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_121 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2036 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2700 GBV_ILN_2817 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4367 GBV_ILN_4392 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 AR 31 2019 5 09 05 1551-1566 |
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10.1007/s11676-019-00964-3 doi (DE-627)SPR040872882 (SPR)s11676-019-00964-3-e DE-627 ger DE-627 rakwb eng 630 640 ASE López-García, José verfasserin aut Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. Illegal logging (dpeaa)DE-He213 Forest density change (dpeaa)DE-He213 Forest recovery (dpeaa)DE-He213 Conifer forests (dpeaa)DE-He213 Monarch Butterfly Biosphere Reserve (dpeaa)DE-He213 Navarro-Cerrillo, Rafael M. verfasserin aut Enthalten in Journal of forestry research Harbin : Univ., 1990 31(2019), 5 vom: 09. Mai, Seite 1551-1566 (DE-627)529093545 (DE-600)2299615-1 1993-0607 nnns volume:31 year:2019 number:5 day:09 month:05 pages:1551-1566 https://dx.doi.org/10.1007/s11676-019-00964-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-FOR SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_121 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2036 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2700 GBV_ILN_2817 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4367 GBV_ILN_4392 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 AR 31 2019 5 09 05 1551-1566 |
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10.1007/s11676-019-00964-3 doi (DE-627)SPR040872882 (SPR)s11676-019-00964-3-e DE-627 ger DE-627 rakwb eng 630 640 ASE López-García, José verfasserin aut Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. Illegal logging (dpeaa)DE-He213 Forest density change (dpeaa)DE-He213 Forest recovery (dpeaa)DE-He213 Conifer forests (dpeaa)DE-He213 Monarch Butterfly Biosphere Reserve (dpeaa)DE-He213 Navarro-Cerrillo, Rafael M. verfasserin aut Enthalten in Journal of forestry research Harbin : Univ., 1990 31(2019), 5 vom: 09. Mai, Seite 1551-1566 (DE-627)529093545 (DE-600)2299615-1 1993-0607 nnns volume:31 year:2019 number:5 day:09 month:05 pages:1551-1566 https://dx.doi.org/10.1007/s11676-019-00964-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-FOR SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_121 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2036 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2700 GBV_ILN_2817 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4367 GBV_ILN_4392 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 AR 31 2019 5 09 05 1551-1566 |
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Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. 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López-García, José |
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López-García, José ddc 630 misc Illegal logging misc Forest density change misc Forest recovery misc Conifer forests misc Monarch Butterfly Biosphere Reserve Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico |
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630 640 ASE Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico Illegal logging (dpeaa)DE-He213 Forest density change (dpeaa)DE-He213 Forest recovery (dpeaa)DE-He213 Conifer forests (dpeaa)DE-He213 Monarch Butterfly Biosphere Reserve (dpeaa)DE-He213 |
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ddc 630 misc Illegal logging misc Forest density change misc Forest recovery misc Conifer forests misc Monarch Butterfly Biosphere Reserve |
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disturbance and forest recovery in the monarch butterfly biosphere reserve, mexico |
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Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico |
| abstract |
Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. |
| abstractGer |
Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. |
| abstract_unstemmed |
Abstract Analysis of the change in forest cover is important to determine stand dynamics and the processes involved in disturbance and recovery. Forests of the core zone of the Monarch Butterfly Biosphere Reserve were studied using photo interpretation techniques, considering biennial changes between 1999 and 2013 and changes over the whole period of study 1999–2013. Error matrices were elaborated to determine the processes of change involved in both recovery and disturbance. The biennial changes for the whole period amounted to 2274 ha; 343 ha accounted as degraded in more than one biennial period. The total changes in forest cover between 1999 and 2013 involved 4902 ha, out of which, 2912 ha were affected by disturbance, and 1990 ha were recovered. For density and 2013 vegetation cover maps, the overall accuracy was 95.6% and 90.2%, respectively. By combining both maps, gradual processes were revealed that were not evident in separate analyses. This methodology is useful for the management and conservation of natural protected areas. |
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Disturbance and forest recovery in the Monarch Butterfly Biosphere Reserve, Mexico |
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| score |
7.399928 |