Soil carbon sequestration potential in semi-arid grasslands in the Conservation Reserve Program

被引:53
|
作者
Li, Chenhui [1 ]
Fultz, Lisa M. [1 ,2 ]
Moore-Kucera, Jennifer [1 ,3 ]
Acosta-Martinez, Veronica [4 ]
Horita, Juske [5 ]
Strauss, Richard [6 ]
Zak, John [6 ]
Calderon, Francisco [7 ]
Weindorf, David [1 ]
机构
[1] Texas Tech Univ, Dept Plant & Soil Sci, POB 42122, Lubbock, TX 79409 USA
[2] Louisiana State Univ AgCtr, Sch Plant Environm & Soil Sci, 104 MB Sturgis, Baton Rouge, LA 70803 USA
[3] USDA NRCS, West Natl Technol Support Ctr, Soil Hlth Div, 1201 NE Lloyd Blvd,Suite 801, Portland, OR 97232 USA
[4] USDA ARS, Cropland Syst Res Lab, 3810 4th St, Lubbock, TX 79415 USA
[5] Texas Tech Univ, Dept Geosci, Box 41053, Lubbock, TX 79409 USA
[6] Texas Tech Univ, Dept Biol Sci, Box 43131, Lubbock, TX 79409 USA
[7] USDA ARS, Cent Great Plains Resources Management Res, 40335 Cty Rd GG, Akron, CO 80720 USA
基金
美国食品与农业研究所;
关键词
C sequestration; Conservation Reserve Program; Soil texture; Soil microbes; MICROBIAL BIOMASS CARBON; LAND-USE CHANGE; ORGANIC-MATTER; ENZYME-ACTIVITIES; ISOTOPE-RATIO; NITROGEN; PLANT; TURNOVER; DYNAMICS; STABILIZATION;
D O I
10.1016/j.geoderma.2017.01.032
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
The Conservation Reserve Program (CRP) in the USA plays a major role in carbon (C) sequestration to help mitigate rising CO2 levels and climate change. The Southern High Plains (SHP) region contains >900.000 ha enrolled in CRP, but a regionally specific C sequestration rate has not been studied, and identification of the C pools and processes important in controlling C sequestration rates remain unresolved. We aimed to address these gaps by utilizing a CRP chronosequence with historical rangeland as a reference ecosystem. Soil samples (0-10 and 10-30 cm) were collected in 2012 and 2014 from a total of 26 fields across seven counties within the SHP and included seven croplands (0 y in CRP), 16 CRP fields that ranged from 6 to 26 y (as of 2012), plus three rangelands. Multiple regression analysis was conducted to gauge the rate of C sequestration under CRP within C pools: soil organic C (SOC), particulate organic matter C (POM-C), and microbial biomass C (MBC), with two additional predictors (soil clay + silt content and precipitation). Despite attempts to control for soil texture by targeting a dominant soil series (Amarillo fine sandy loam), the percent of clay + silt (15.2-48.7%) significantly influenced C accrual. The C sources (C-3 from previous cropping systems or C-4 from CRP grasses) in SOC and POMC were assessed using stable C isotope signatures. Additionally, the role of soil microbes in C sequestration was evaluated by investigating the relationship between MBC and CO2 flux and C sequestration. SOC increased at a rate of 69.82 and 132.87 kg C ha(-1) y(-1) and would take approximately 74 and 77 y to reach the rangeland C stocks at 0-10 and 0-30 cm, respectively. The C-4-C primarily from the introduced grasses was the main source of C sequestration. SOC gains were essentially due to increases in POM-C and MBC, accounting for 50.04 and 15.64% of SOC sequestration at 0-30 cm, respectively. The highest semi-partial correlation coefficients between the increasing years under CRP restoration and MBC indicated CRP had the strongest effect on MBC compared to other C pools. In addition, increasing soil CO2 flux and MBC:SOC ratio with years of CRP restoration indicated MBC played a critical role in the C sequestration process. Conservation of CRP lands and efforts to sustain perennial systems in this highly erodible landscape should be a high priority of conservation programs. In doing so, significant offsets to increasing atmospheric CO2 levels may be achieved in addition to erosion control and improved wildlife habitat. (C) 2017 Elsevier B.V. All rights reserved.
引用
收藏
页码:80 / 90
页数:11
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