Modeling carbon dynamics in vegetation and soil under the impact of soil erosion and deposition

被引:192
作者
Liu, SG [1 ]
Bliss, N
Sundquist, E
Huntington, TG
机构
[1] US Geol Survey, Earth Resources Syst Observat Data Ctr, SAIC, Sioux Falls, SD 57198 USA
[2] US Geol Survey, Woods Hole, MA 02543 USA
[3] US Geol Survey, Augusta, ME 04330 USA
关键词
carbon dynamics; model simulations; EDCM model; erosion; deposition;
D O I
10.1029/2002GB002010
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Soil erosion and deposition may play important roles in balancing the global atmospheric carbon budget through their impacts on the net exchange of carbon between terrestrial ecosystems and the atmosphere. Few models and studies have been designed to assess these impacts. In this study, we developed a general ecosystem model, Erosion-Deposition-Carbon-Model (EDCM), to dynamically simulate the influences of rainfall-induced soil erosion and deposition on soil organic carbon (SOC) dynamics in soil profiles. EDCM was applied to several landscape positions in the Nelson Farm watershed in Mississippi, including ridge top ( without erosion or deposition), eroding hillslopes, and depositional sites that had been converted from native forests to croplands in 1870. Erosion reduced the SOC storage at the eroding sites and deposition increased the SOC storage at the depositional areas compared with the site without erosion or deposition. Results indicated that soils were consistently carbon sources to the atmosphere at all landscape positions from 1870 to 1950, with lowest source strength at the eroding sites (13 to 24 gC m(-2) yr(-1)), intermediate at the ridge top (34 gC m(-2) yr(-1)), and highest at the depositional sites (42 to 49 gC m(-2) yr(-1)). During this period, erosion reduced carbon emissions via dynamically replacing surface soil with subsurface soil that had lower SOC contents (quantity change) and higher passive SOC fractions (quality change). Soils at all landscape positions became carbon sinks from 1950 to 1997 due to changes in management practices (e.g., intensification of fertilization and crop genetic improvement). The sink strengths were highest at the eroding sites (42 to 44 gC m(-2) yr(-1)), intermediate at the ridge top (35 gC m(-2) yr(-1)), and lowest at the depositional sites (26 to 29 gC m(-2) yr(-1)). During this period, erosion enhanced carbon uptake at the eroding sites by continuously taking away a fraction of SOC that can be replenished with enhanced plant residue input. Overall, soil erosion and deposition reduced CO2 emissions from the soil into the atmosphere by exposing low carbon-bearing soil at eroding sites and by burying SOC at depositional sites. The results suggest that failing to account for the impact of soil erosion and deposition may potentially contribute to an overestimation of both the total historical carbon released from soils owing to land use change and the contemporary carbon sequestration rates at the eroding sites.
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页数:24
相关论文
共 76 条
[1]   GENETIC IMPROVEMENTS IN WINTER-WHEAT YIELDS SINCE 1900 AND ASSOCIATED PHYSIOLOGICAL-CHANGES [J].
AUSTIN, RB ;
BINGHAM, J ;
BLACKWELL, RD ;
EVANS, LT ;
FORD, MA ;
MORGAN, CL ;
TAYLOR, M .
JOURNAL OF AGRICULTURAL SCIENCE, 1980, 94 (JUN) :675-689
[2]   Strategies for measuring and modelling carbon dioxide and water vapour fluxes over terrestrial ecosystems [J].
Baldocchi, D ;
Valentini, R ;
Running, S ;
Oechel, W ;
Dahlman, R .
GLOBAL CHANGE BIOLOGY, 1996, 2 (03) :159-168
[3]  
Bouwman A. F., 1989, Land Degradation & Rehabilitation, V1, P125, DOI 10.1002/ldr.3400010205
[4]   Changing role of cultivated land in the global carbon cycle [J].
Buyanovsky, GA ;
Wagner, GH .
BIOLOGY AND FERTILITY OF SOILS, 1998, 27 (03) :242-245
[5]   POSTHARVEST RESIDUE INPUT TO CROPLAND [J].
BUYANOVSKY, GA ;
WAGNER, GH .
PLANT AND SOIL, 1986, 93 (01) :57-65
[6]   Carbon cycling in cultivated land and its global significance [J].
Buyanovsky, GA ;
Wagner, GH .
GLOBAL CHANGE BIOLOGY, 1998, 4 (02) :131-141
[7]   An integrated terrestrial ecosystem carbon-budget model based on changes in disturbance, climate, and atmospheric chemistry [J].
Chen, WJ ;
Chen, J ;
Cihlar, J .
ECOLOGICAL MODELLING, 2000, 135 (01) :55-79
[8]  
CIHACEK LJ, 1994, J SOIL WATER CONSERV, V49, P259
[9]   Source type ascription for fluvial suspended sediment based on a quantitative composite fingerprinting technique [J].
Collins, AL ;
Walling, DE ;
Leeks, GJL .
CATENA, 1997, 29 (01) :1-27
[10]   GENETIC-IMPROVEMENT IN AGRONOMIC TRAITS OF HARD RED WINTER-WHEAT CULTIVARS FROM 1919 TO 1987 [J].
COX, TS ;
SHROYER, JP ;
LIU, BH ;
SEARS, RG ;
MARTIN, TJ .
CROP SCIENCE, 1988, 28 (05) :756-760