Influence of spatially dependent, modeled soil carbon emission factors on life-cycle greenhouse gas emissions of corn and cellulosic ethanol

被引:40
作者
Qin, Zhangcai [1 ]
Dunn, Jennifer B. [1 ]
Kwon, Hoyoung [2 ]
Mueller, Steffen [3 ]
Wander, Michelle M. [4 ]
机构
[1] Argonne Natl Lab, Div Energy Syst, 9700 South Cass Ave, Argonne, IL 60439 USA
[2] Int Food Policy Res Inst, Environm & Prod Technol Div, 2033 K St NW, Washington, DC 20006 USA
[3] Univ Illinois, Energy Resources Ctr, 1309 South Halsted St, Chicago, IL 60607 USA
[4] Univ Illinois, Dept Nat Resources & Environm Sci, 1102 South Goodwin Ave, Urbana, IL 61801 USA
来源
GLOBAL CHANGE BIOLOGY BIOENERGY | 2016年 / 8卷 / 06期
基金
美国能源部;
关键词
GREET model; land use change; life cycle analysis; Miscanthus; poplar; surrogate CENTURY model; switchgrass; willow; LAND-USE CHANGE; CROP RESIDUE; US CROPLANDS; BIOFUELS; IMPACT; BIOENERGY; SEQUESTRATION; EXPANSION; STOCKS; YIELD;
D O I
10.1111/gcbb.12333
中图分类号
S3 [农学(农艺学)];
学科分类号
0901 ;
摘要
Converting land to biofuel feedstock production incurs changes in soil organic carbon (SOC) that can influence biofuel life-cycle greenhouse gas (GHG) emissions. Estimates of these land use change (LUC) and life-cycle GHG emissions affect biofuels' attractiveness and eligibility under a number of renewable fuel policies in the USA and abroad. Modeling was used to refine the spatial resolution and depth extent of domestic estimates of SOC change for land (cropland, cropland pasture, grassland, and forest) conversion scenarios to biofuel crops (corn, corn stover, switchgrass, Miscanthus, poplar, and willow) at the county level in the USA. Results show that in most regions, conversions from cropland and cropland pasture to biofuel crops led to neutral or small levels of SOC sequestration, while conversion of grassland and forest generally caused net SOC loss. SOC change results were incorporated into the Greenhouse Gases, Regulated Emissions, and Energy use in Transportation (GREET) model to assess their influence on life-cycle GHG emissions of corn and cellulosic ethanol. Total LUC GHG emissions (g CO(2)eq MJ(-1)) were 2.1-9.3 for corn-, -0.7 for corn stover-, -3.4 to 12.9 for switchgrass-, and -20.1 to -6.2 for Miscanthus ethanol; these varied with SOC modeling assumptions applied. Extending the soil depth from 30 to 100 cm affected spatially explicit SOC change and overall LUC GHG emissions; however, the influence on LUC GHG emission estimates was less significant in corn and corn stover than cellulosic feedstocks. Total life-cycle GHG emissions (g CO(2)eq MJ(-1), 100 cm) were estimated to be 59-66 for corn ethanol, 14 for stover ethanol, 18-26 for switchgrass ethanol, and -7 to -0.6 for Miscanthus ethanol. The LUC GHG emissions associated with poplar-and willow-derived ethanol may be higher than that for switchgrass ethanol due to lower biomass yield.
引用
收藏
页码:1136 / 1149
页数:14
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