Biochar persistence, priming and microbial responses to pyrolysis temperature series

被引:77
作者
Budai, Alice [1 ,2 ]
Rasse, Daniel P. [1 ]
Lagomarsino, Alessandra [3 ]
Lerch, Thomas Z. [4 ]
Paruch, Lisa [1 ]
机构
[1] Norwegian Inst Bioecon Res, Dept Soil Qual & Climate Change, Hogskoleveien 7, N-1430 As, Norway
[2] Norwegian Univ Life Sci, Dept Environm Sci, Box 5003, N-1432 As, Norway
[3] Consiglio Ric Agr & Anal Econ Agr, Agrobiol & Pedol Res Ctr CRA ABP, Piazza M dAzeglio 30, I-50121 Florence, Italy
[4] UPEC, Inst Ecol & Environm Sci IEES Paris, F-94010 Creteil, France
关键词
Slow pyrolysis; Hydrothermal carbonization; Hydrochar; Flash carbonization; Microbial community composition; SOIL ORGANIC-MATTER; HYDROTHERMAL CARBONIZATION; BACTERIAL COMMUNITIES; CHEMICAL-COMPOSITION; AGRICULTURAL SOIL; CARBON-DIOXIDE; STABILITY; MINERALIZATION; BIOMASS; DIVERSITY;
D O I
10.1007/s00374-016-1116-6
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Biochar and its properties can be significantly altered according to how it is produced, and this has ramifications towards how biochar behaves once added to soil. We produced biochars from corncob and miscanthus straw via different methods (slow pyrolysis, hydrothermal and flash carbonization) and temperatures to assess how carbon cycling and soil microbial communities were affected. Mineralization of biochar, its parent feedstock, and native soil organic matter were monitored using C-13 natural abundance during a 1-year lab incubation. Bacterial and fungal community compositions were studied using T-RFLP and ARISA, respectively. We found that persistent biochar-C with a half-life 60 times higher than the parent feedstock can be achieved at pyrolysis temperatures of as low as 370 A degrees C, with no further gains to be made at higher temperatures. Biochar re-applied to soil previously incubated with our highest temperature biochar mineralized faster than when applied to unamended soil. Positive priming of native SOC was observed for all amendments but subsided by the end of the incubation. Fungal and bacterial community composition of the soil-biochar mixture changed increasingly with the application of biochars produced at higher temperatures as compared to unamended soil. Those changes were significantly (P < 0.005) related to biochar properties (mainly pH and O/C) and thus were correlated to pyrolysis temperature. In conclusion, our results suggest that biochar produced at temperatures as low as 370 A degrees C can be utilized to sequester C in soil for more than 100 years while having less impact on soil microbial activities than high-temperature biochars.
引用
收藏
页码:749 / 761
页数:13
相关论文
共 66 条
[61]  
White TJ., 1990, PCR protocols: a guide to methods and applications, V18, P315, DOI DOI 10.1016/B978-0-12-372180-8.50042-1
[62]   Predicting pyrogenic organic matter mineralization from its initial properties and implications for carbon management [J].
Whitman, Thea ;
Hanley, Kelly ;
Enders, Akio ;
Lehmann, Johannes .
ORGANIC GEOCHEMISTRY, 2013, 64 :76-83
[63]   Sustainable biochar to mitigate global climate change [J].
Woolf, Dominic ;
Amonette, James E. ;
Street-Perrott, F. Alayne ;
Lehmann, Johannes ;
Joseph, Stephen .
NATURE COMMUNICATIONS, 2010, 1
[64]   The forms of alkalis in the biochar produced from crop residues at different temperatures [J].
Yuan, Jin-Hua ;
Xu, Ren-Kou ;
Zhang, Hong .
BIORESOURCE TECHNOLOGY, 2011, 102 (03) :3488-3497
[65]   Effects of pyrolysis temperature and heating time on biochar obtained from the pyrolysis of straw and lignosulfonate [J].
Zhang, Jie ;
Liu, Jia ;
Liu, Rongle .
BIORESOURCE TECHNOLOGY, 2015, 176 :288-291
[66]   Positive and negative carbon mineralization priming effects among a variety of biochar-amended soils [J].
Zimmerman, Andrew R. ;
Gao, Bin ;
Ahn, Mi-Youn .
SOIL BIOLOGY & BIOCHEMISTRY, 2011, 43 (06) :1169-1179