Initial soil C and land-use history determine soil C sequestration under perennial bioenergy crops

被引:38
|
作者
Rowe, Rebecca L. [1 ,2 ]
Keith, Aidan M. [1 ]
Elias, Dafydd [1 ]
Dondini, Marta [3 ]
Smith, Pete [3 ]
Oxley, Jonathan [1 ]
McNamara, Niall P. [1 ]
机构
[1] Lancaster Environm Ctr, Ctr Ecol & Hydrol, Lib Ave, Lancaster LA1 4AP, England
[2] Univ Edinburgh, Sch GeoSci, Kings Bldg,Alexander Crum Brown Rd, Edinburgh EH9 3FF, Midlothian, Scotland
[3] Univ Aberdeen, Inst Biol & Environm Sci, 23 St Machar Dr, Aberdeen AB24 3UU, Scotland
来源
GLOBAL CHANGE BIOLOGY BIOENERGY | 2016年 / 8卷 / 06期
关键词
bioenergy; Carbon Stocks; land-use change; Miscanthus; soil carbon; SRC willow; CARBON STOCKS; ORGANIC-CARBON; SPATIAL VARIABILITY; POPLAR PLANTATIONS; MISCANTHUS; AFFORESTATION; GRASSLAND; IMPACT; MITIGATION; STABILITY;
D O I
10.1111/gcbb.12311
中图分类号
S3 [农学(农艺学)];
学科分类号
0901 ;
摘要
In the UK and other temperate regions, short rotation coppice (SRC) and Miscanthus x giganteus (Miscanthus) are two of the leading 'second-generation' bioenergy crops. Grown specifically as a low-carbon (C) fossil fuel replacement, calculations of the climate mitigation provided by these bioenergy crops rely on accurate data. There are concerns that uncertainty about impacts on soil C stocks of transitions from current agricultural land use to these bioenergy crops could lead to either an under-or overestimate of their climate mitigation potential. Here, for locations across mainland Great Britain (GB), a paired-site approach and a combination of 30-cm- and 1-m-deep soil sampling were used to quantify impacts of bioenergy land-use transitions on soil C stocks in 41 commercial land-use transitions; 12 arable to SRC, 9 grasslands to SRC, 11 arable to Miscanthus and 9 grasslands to Miscanthus. Mean soil C stocks were lower under both bioenergy crops than under the grassland controls but only significant at 0-30 cm. Mean soil C stocks at 0-30 cm were 33.55 +/- 7.52 Mg C ha(-1) and 26.83 +/- 8.08 Mg C ha(-1) lower under SRC (P = 0.004) and Miscanthus plantations (P = 0.001), respectively. Differences between bioenergy crops and arable controls were not significant in either the 30-cm or 1-m soil cores and smaller than for transitions from grassland. No correlation was detected between change in soil C stock and bioenergy crop age (time since establishment) or soil texture. Change in soil C stock was, however, negatively correlated with the soil C stock in the original land use. We suggest, therefore, that selection of sites for bioenergy crop establishment with lower soil C stocks, most often under arable land use, is the most likely to result in increased soil C stocks.
引用
收藏
页码:1046 / 1060
页数:15
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