000 04012aam a2200697 4500
999 _c119184
_d119184
003 CR-TuBCO
005 20220427175715.0
007 ta
008 141204t1999 xxu||||| |||| 00| 0 eng d
022 _a0012-9658
040 _aCR-TuBCO
_cCR-TuBCO
_bspa
041 0 _aeng
100 1 _967940
_aFlint Hughes, R.
_uDepartment of Forest Science, Oregon State University, USA
245 1 0 _aBiomass, carbon and nutrient dynamics of secondary forests in a humid tropical region of México
260 _aWashington, DC
_bEcological Society of America
_c1999
270 _aSan José, C.R.
300 _a16 páginas
_bIncluye 3 figuras y 7 tablas
504 _aBibliografía en las páginas1906-1907
520 _aTropical secondary forests have the capacity to function as large carbon and nutrient sinks and may offset losses resulting from deforestation and land use. Total aboveground biomass (TAGB) increased with increasing site age and ranged from 4.8 Mg/ha in a recently abandoned site to 287 Mg/ha in the 50-yr-old secondary forest site. Results indicate that secondary forests would reach TAGB levels equivalent to those of primary forests in the Los Tuxtlas Region after 73 yr. Furthermore, mean annual aboveground biomass accumulation (ABA) of secondary forests was strongly and inversely related to the duration of prior land use. Aboveground pools of C, N, S, and P were also positively correlated with secondary forest age. For forests between 6 mo and 50 yr of age, C pools increased from 2 to 136 Mg/ha, N increased from 72 to 1167 kg/ha, S increased from 9 to 147 kg/ha, and P increased from 5 to 147 kg/ha. In contrast, C, N, and S pools in mineral soil to a 1-m depth remained relatively stable throughout the successional chronosequence and averaged 207, 20, and 3.4 Mg/ha, respectively. Dynamics of the combined aboveground and mineral soil C pools were characterized by increasing contributions from aboveground pools with increasing forest age; aboveground C pools accounted for 9% and 42% of the combined pool in the youngest and oldest forests, respectively. In contrast, changes in combined aboveground and mineral soil pools of N and S during secondary succession were relatively small because >90% of N and S mass was located in mineral soil pools.
650 1 4 _9138293
_aBOSQUE SECUNDARIO
650 1 4 _9138300
_aBOSQUE TROPICAL
650 1 4 _9165549
_aSUCESION ECOLOGICA
650 1 4 _9139477
_aCARBONO
650 1 4 _9164156
_aSECUESTRO DE CARBONO
650 1 4 _9137963
_aBIOMASA
650 1 4 _9154288
_aMEDICION
650 1 4 _9135462
_aALOMETRIA
650 1 4 _9155109
_a MODELOS
650 1 4 _9154241
_aMECANICA DEL SUELO
650 1 4 _9151861
_aINTERACCIONES NUTRIENTE NUTRIENTE
650 1 4 _9167870
_aUTILIZACION DE LA TIERRA
650 1 4 _9148954
_aGASES DE EFECTO INVERNADERO
650 1 4 _9145225
_aECUACIONES ALOMETRICAS
650 1 4 _9137963
_aBIOMASA
650 1 0 _9337698
_aSECONDARY FORESTS
650 1 0 _aTROPICAL FORESTS
_9341801
650 1 0 _9315958
_aECOLOGICAL SUCCESSION
650 1 0 _aCARBON
_9139459
650 1 0 _aBIOMASS
_9137969
650 1 0 _aMEASUREMENT
_9154228
650 1 0 _aMODELS
_9327554
650 1 0 _9338928
_aSOIL MECHANICS
650 1 0 _9328927
_aNUTRIENT NUTRIENT INTERACTIONS
650 1 0 _aLAND USE
_9152641
650 1 0 _aGREENHOUSE GASES
_9149687
651 0 _aMÉXICO
_92173
700 _950067
_aBoone Kauffman, J.
_c autor/a
_uDepartment of Fisheries and Wildlife, Oregon State University, USA
700 _980603
_aJaramillo, Víctor J.
_c autor/a
_uUniversidad Nacional Autónoma de México, México
830 _aEcology (EUA)
_nnúmero 6
_pSeptiembre (1999)
_ppáginas 1892-1907
_vVolumen 80
856 _qpdf
_uhttps://esajournals.onlinelibrary.wiley.com/doi/10.1890/0012-9658%281999%29080%5B1892%3ABCANDO%5D2.0.CO%3B2
_yeng
901 _aP35
902 _aP33
903 _aE
903 _aV
904 _aklines
905 _aC
906 _a20051207
_b20051207
908 _aJ
942 _cANA
_2z