Factors affecting utilisation of atmospheric CO by soils

被引:39
作者
Moxley, JM
Smith, KA
机构
[1] Univ Edinburgh, Inst Ecol & Resource Management, Edinburgh EH9 3JG, Midlothian, Scotland
[2] Scottish Agr Coll, Dept Soils, Edinburgh EH9 3JG, Midlothian, Scotland
基金
英国自然环境研究理事会;
关键词
D O I
10.1016/S0038-0717(97)00095-3
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Carbon monoxide is an important atmospheric trace gas because it is the main atmospheric sink for the hydroxyl radical. Nevertheless, about a fifth of CO is utilised by soil microorganisms. As the strengths of sources and sinks are currently finely balanced, any change in the strength of the soil sink would lead to changes in the tropospheric CO concentration, which could in turn affect the concentration of radiatively active trace gases such as methane. The factors affecting the rate of CO utilisation by soils have been investigated in laboratory incubations, and in the field using static chambers. Laboratory incubations showed that there was a strong positive correlation between total organic carbon (TOC) content and CO utilisation by soils. The amount of microbial biomass carbon was strongly correlated with TOC content. Rates: of CO utilisation by woodland soils were faster than by adjacent arable soils, reflecting the importance of differences in TOC content. Further investigation showed that there was an optimum water content for utilisation for each soil at approximately field capacity. Field measurements showed that temperature was the most important factor affecting CO utilisation rates at any one site. In several cases there was a negative relationship between CO uptake rate and temperature which was attributed to simultaneous CO production from the surface litter layer. In contrast, a fallow arable soil showed an optimum rate at approximately 10 degrees C. (C) 1997 Elsevier Science Ltd.
引用
收藏
页码:65 / 79
页数:15
相关论文
共 39 条
[1]   MICROBIAL-METABOLISM OF CARBON-MONOXIDE IN CULTURE AND IN SOIL [J].
BARTHOLOMEW, GW ;
ALEXANDER, M .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1979, 37 (05) :932-937
[2]  
BENDER M, 1994, BIOGEOCHEMISTRY, V27, P97, DOI 10.1007/BF00002813
[3]  
BEST E K, 1976, Queensland Journal of Agricultural and Animal Sciences, V33, P161
[4]  
CONRAD R, 1988, ADV MICROB ECOL, V10, P231
[5]  
Conrad R., 1985, Planetary ecology, P112
[6]   ROLE OF MICROORGANISMS IN THE CONSUMPTION AND PRODUCTION OF ATMOSPHERIC CARBON-MONOXIDE BY SOIL [J].
CONRAD, R ;
SEILER, W .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1980, 40 (03) :437-445
[7]   CHARACTERISTICS OF ABIOLOGICAL CARBON-MONOXIDE FORMATION FROM SOIL ORGANIC-MATTER, HUMIC ACIDS, AND PHENOLIC-COMPOUNDS [J].
CONRAD, R ;
SEILER, W .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1985, 19 (12) :1165-1169
[8]   ROLE OF CARBOXYDOBACTERIA IN CONSUMPTION OF ATMOSPHERIC CARBON-MONOXIDE BY SOIL [J].
CONRAD, R ;
MEYER, O ;
SEILER, W .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1981, 42 (02) :211-215
[9]   INFLUENCE OF TEMPERATURE, MOISTURE, AND ORGANIC-CARBON ON THE FLUX OF H-2 AND CO BETWEEN SOIL AND ATMOSPHERE - FIELD STUDIES IN SUB-TROPICAL REGIONS [J].
CONRAD, R ;
SEILER, W .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 1985, 90 (ND3) :5699-5709
[10]   ARID SOILS AS A SOURCE OF ATMOSPHERIC CARBON-MONOXIDE [J].
CONRAD, R ;
SEILER, W .
GEOPHYSICAL RESEARCH LETTERS, 1982, 9 (12) :1353-1356