Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon
Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest syste...
Ausführliche Beschreibung
Autor*in: |
Silva, Antonio Kledson Leal [verfasserIn] Vasconcelos, Steel Silva [verfasserIn] de Carvalho, Claudio José Reis [verfasserIn] Cordeiro, Iracema Maria Castro Coimbra [verfasserIn] |
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Format: |
E-Artikel |
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Sprache: |
Englisch |
Erschienen: |
2011 |
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Schlagwörter: |
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Übergeordnetes Werk: |
Enthalten in: Plant and soil - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1948, 347(2011), 1-2 vom: 15. Juni, Seite 377-386 |
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Übergeordnetes Werk: |
volume:347 ; year:2011 ; number:1-2 ; day:15 ; month:06 ; pages:377-386 |
Links: |
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DOI / URN: |
10.1007/s11104-011-0857-0 |
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Katalog-ID: |
SPR016722965 |
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520 | |a Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. | ||
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650 | 4 | |a Regrowth forest |7 (dpeaa)DE-He213 | |
700 | 1 | |a Vasconcelos, Steel Silva |e verfasserin |4 aut | |
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10.1007/s11104-011-0857-0 doi (DE-627)SPR016722965 (SPR)s11104-011-0857-0-e DE-627 ger DE-627 rakwb eng 570 580 ASE 48.32 bkl 48.52 bkl Silva, Antonio Kledson Leal verfasserin aut Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. Amazon (dpeaa)DE-He213 Decomposition (dpeaa)DE-He213 Litter (dpeaa)DE-He213 Fine root (dpeaa)DE-He213 Regrowth forest (dpeaa)DE-He213 Vasconcelos, Steel Silva verfasserin aut de Carvalho, Claudio José Reis verfasserin aut Cordeiro, Iracema Maria Castro Coimbra verfasserin aut Enthalten in Plant and soil Dordrecht [u.a.] : Springer Science + Business Media B.V, 1948 347(2011), 1-2 vom: 15. Juni, Seite 377-386 (DE-627)270934979 (DE-600)1478535-3 1573-5036 nnns volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 https://dx.doi.org/10.1007/s11104-011-0857-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 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_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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 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_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_4393 GBV_ILN_4700 48.32 ASE 48.52 ASE AR 347 2011 1-2 15 06 377-386 |
spelling |
10.1007/s11104-011-0857-0 doi (DE-627)SPR016722965 (SPR)s11104-011-0857-0-e DE-627 ger DE-627 rakwb eng 570 580 ASE 48.32 bkl 48.52 bkl Silva, Antonio Kledson Leal verfasserin aut Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. Amazon (dpeaa)DE-He213 Decomposition (dpeaa)DE-He213 Litter (dpeaa)DE-He213 Fine root (dpeaa)DE-He213 Regrowth forest (dpeaa)DE-He213 Vasconcelos, Steel Silva verfasserin aut de Carvalho, Claudio José Reis verfasserin aut Cordeiro, Iracema Maria Castro Coimbra verfasserin aut Enthalten in Plant and soil Dordrecht [u.a.] : Springer Science + Business Media B.V, 1948 347(2011), 1-2 vom: 15. Juni, Seite 377-386 (DE-627)270934979 (DE-600)1478535-3 1573-5036 nnns volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 https://dx.doi.org/10.1007/s11104-011-0857-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 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_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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 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_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_4393 GBV_ILN_4700 48.32 ASE 48.52 ASE AR 347 2011 1-2 15 06 377-386 |
allfields_unstemmed |
10.1007/s11104-011-0857-0 doi (DE-627)SPR016722965 (SPR)s11104-011-0857-0-e DE-627 ger DE-627 rakwb eng 570 580 ASE 48.32 bkl 48.52 bkl Silva, Antonio Kledson Leal verfasserin aut Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. Amazon (dpeaa)DE-He213 Decomposition (dpeaa)DE-He213 Litter (dpeaa)DE-He213 Fine root (dpeaa)DE-He213 Regrowth forest (dpeaa)DE-He213 Vasconcelos, Steel Silva verfasserin aut de Carvalho, Claudio José Reis verfasserin aut Cordeiro, Iracema Maria Castro Coimbra verfasserin aut Enthalten in Plant and soil Dordrecht [u.a.] : Springer Science + Business Media B.V, 1948 347(2011), 1-2 vom: 15. Juni, Seite 377-386 (DE-627)270934979 (DE-600)1478535-3 1573-5036 nnns volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 https://dx.doi.org/10.1007/s11104-011-0857-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 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_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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 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_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_4393 GBV_ILN_4700 48.32 ASE 48.52 ASE AR 347 2011 1-2 15 06 377-386 |
allfieldsGer |
10.1007/s11104-011-0857-0 doi (DE-627)SPR016722965 (SPR)s11104-011-0857-0-e DE-627 ger DE-627 rakwb eng 570 580 ASE 48.32 bkl 48.52 bkl Silva, Antonio Kledson Leal verfasserin aut Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. Amazon (dpeaa)DE-He213 Decomposition (dpeaa)DE-He213 Litter (dpeaa)DE-He213 Fine root (dpeaa)DE-He213 Regrowth forest (dpeaa)DE-He213 Vasconcelos, Steel Silva verfasserin aut de Carvalho, Claudio José Reis verfasserin aut Cordeiro, Iracema Maria Castro Coimbra verfasserin aut Enthalten in Plant and soil Dordrecht [u.a.] : Springer Science + Business Media B.V, 1948 347(2011), 1-2 vom: 15. Juni, Seite 377-386 (DE-627)270934979 (DE-600)1478535-3 1573-5036 nnns volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 https://dx.doi.org/10.1007/s11104-011-0857-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 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_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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 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_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_4393 GBV_ILN_4700 48.32 ASE 48.52 ASE AR 347 2011 1-2 15 06 377-386 |
allfieldsSound |
10.1007/s11104-011-0857-0 doi (DE-627)SPR016722965 (SPR)s11104-011-0857-0-e DE-627 ger DE-627 rakwb eng 570 580 ASE 48.32 bkl 48.52 bkl Silva, Antonio Kledson Leal verfasserin aut Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. Amazon (dpeaa)DE-He213 Decomposition (dpeaa)DE-He213 Litter (dpeaa)DE-He213 Fine root (dpeaa)DE-He213 Regrowth forest (dpeaa)DE-He213 Vasconcelos, Steel Silva verfasserin aut de Carvalho, Claudio José Reis verfasserin aut Cordeiro, Iracema Maria Castro Coimbra verfasserin aut Enthalten in Plant and soil Dordrecht [u.a.] : Springer Science + Business Media B.V, 1948 347(2011), 1-2 vom: 15. Juni, Seite 377-386 (DE-627)270934979 (DE-600)1478535-3 1573-5036 nnns volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 https://dx.doi.org/10.1007/s11104-011-0857-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 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_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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 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_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_4393 GBV_ILN_4700 48.32 ASE 48.52 ASE AR 347 2011 1-2 15 06 377-386 |
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English |
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Enthalten in Plant and soil 347(2011), 1-2 vom: 15. Juni, Seite 377-386 volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 |
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Enthalten in Plant and soil 347(2011), 1-2 vom: 15. Juni, Seite 377-386 volume:347 year:2011 number:1-2 day:15 month:06 pages:377-386 |
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Amazon Decomposition Litter Fine root Regrowth forest |
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Plant and soil |
authorswithroles_txt_mv |
Silva, Antonio Kledson Leal @@aut@@ Vasconcelos, Steel Silva @@aut@@ de Carvalho, Claudio José Reis @@aut@@ Cordeiro, Iracema Maria Castro Coimbra @@aut@@ |
publishDateDaySort_date |
2011-06-15T00:00:00Z |
hierarchy_top_id |
270934979 |
dewey-sort |
3570 |
id |
SPR016722965 |
language_de |
englisch |
fullrecord |
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To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). 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|
author |
Silva, Antonio Kledson Leal |
spellingShingle |
Silva, Antonio Kledson Leal ddc 570 bkl 48.32 bkl 48.52 misc Amazon misc Decomposition misc Litter misc Fine root misc Regrowth forest Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon |
authorStr |
Silva, Antonio Kledson Leal |
ppnlink_with_tag_str_mv |
@@773@@(DE-627)270934979 |
format |
electronic Article |
dewey-ones |
570 - Life sciences; biology 580 - Plants (Botany) |
delete_txt_mv |
keep |
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aut aut aut aut |
collection |
springer |
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illustrated |
Not Illustrated |
issn |
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570 580 ASE 48.32 bkl 48.52 bkl Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon Amazon (dpeaa)DE-He213 Decomposition (dpeaa)DE-He213 Litter (dpeaa)DE-He213 Fine root (dpeaa)DE-He213 Regrowth forest (dpeaa)DE-He213 |
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ddc 570 bkl 48.32 bkl 48.52 misc Amazon misc Decomposition misc Litter misc Fine root misc Regrowth forest |
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ddc 570 bkl 48.32 bkl 48.52 misc Amazon misc Decomposition misc Litter misc Fine root misc Regrowth forest |
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ddc 570 bkl 48.32 bkl 48.52 misc Amazon misc Decomposition misc Litter misc Fine root misc Regrowth forest |
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title |
Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon |
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Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon |
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Silva, Antonio Kledson Leal |
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Plant and soil |
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Silva, Antonio Kledson Leal Vasconcelos, Steel Silva de Carvalho, Claudio José Reis Cordeiro, Iracema Maria Castro Coimbra |
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title_sort |
litter dynamics and fine root production in schizolobium parahyba var. amazonicum plantations and regrowth forest in eastern amazon |
title_auth |
Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon |
abstract |
Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. |
abstractGer |
Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. |
abstract_unstemmed |
Abstract Forest plantations and agroforestry systems with Schizolobium parahyba var. amazonicum have greatly expanded in the Brazilian Amazon, generally as an alternative for reforesting degraded areas. To our knowledge there are no reports of above- and below-ground production in these forest systems. We quantified litter and fine root production in 6-yr old Schizolobium-based plantation forests (monospecific: MON, mixture: MIX, and agroforestry system: AFS) and in ~25-yr old regrowth forest (REG) over 8–12 months. We used litter traps and ingrowth cores to quantify litter and fine root production, respectively. Annual litter production was significantly lower in Schizolobium-based plantations (mean ± standard error, MON = 5.92 ± 0.15, MIX = 6.08 ± 0.13, AFS = 6.63 ± 0.13 Mg $ ha^{−1} $ $ year^{−1} $) than in regrowth forest (8.64 ± 0.08 Mg $ ha^{−1} $ $ year^{−1} $). Schizolobium-based plantations showed significantly higher litter stock (MON = 7.7 ± 1.0, MIX = 7.4 ± 0.1 Mg $ ha^{−1} $) than REG (5.9 ± 1.3 Mg $ ha^{−1} $). Total fine root production over an 8-month period was significantly higher in Schizolobium-based plantations (MON = 3.8 ± 0.2, MIX = 3.4 ± 0.2, AFS = 2.7 ± 0.1 Mg $ ha^{−1} $) than in REG (1.1 ± 0.03 Mg $ ha^{−1} $). Six-yr old Schizolobium-based plantations and ~25-yr old regrowth forests showed comparable rates of litter + fine root production, suggesting that young forest plantations may be an interesting alternative to restore degraded areas due to early reestablishment of organic matter cycling under the studied conditions. |
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Litter dynamics and fine root production in Schizolobium parahyba var. amazonicum plantations and regrowth forest in Eastern Amazon |
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score |
7.398164 |