Storage effects on the community level physiological profiles of Mediterranean forest soils

被引:20
作者
Goberna, M
Insam, H
Pascual, JA
Sánchez, J
机构
[1] Univ Valencia, CSIC, Ctr Invest Desertificat, Valencia 46470, Spain
[2] Inst Microbiol, A-6020 Innsbruck, Austria
[3] CEBAS, CSIC, Murcia 30080, Spain
关键词
community level physiological profiles; storage effects; Mediterranean forest soils;
D O I
10.1016/j.soilbio.2004.06.014
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Community level physiological profiles (CLPPs) have been implemented in many European soil monitoring programmes as a rapid tool for the assessment of the functional properties of soil microbial communities. However, this technique has not been harmonized among different laboratories. In this experiment, the changes of the CLPPs after storage of three Mediterranean forest soils were characterised for two sampling depths. The methods to store the samples were cooling, freezing and room temperature storage. Data presented in this study provide evidence that substantial changes can occur to the soil microbial community functions, regardless of the kind of storage. Changes in functional diversity and substrate evenness depended on the profile and sampling depth. The rate of consumption of the groups of substrates, however, shifted towards an enhanced utilisation of carboxylic acids, phenols and/or amines after 1 month storage at 4 C, regardless of the profile or sampling depth. This was attributed to the physical disruption of soil aggregates and exposure of relatively recalcitrant occluded organic matter. These effects levelled out during 1-year storage. The great sensitivity of CLPPs to storage treatment suggests to take care for immediate analysis after sampling. In case fresh samples are not available, freezing is recommended as a convenient alternative; in that case, however, the kinetic approach is required for data analysis. (C) 2005 Elsevier Ltd. All rights reserved.
引用
收藏
页码:173 / 178
页数:6
相关论文
共 24 条
[1]   Organic species in ped surface and core fractions along a climosequence in the prairie, North America [J].
Amelung, W ;
Zech, W .
GEODERMA, 1996, 74 (3-4) :193-206
[2]  
[Anonymous], 1998, KEYS SOIL TAX
[3]  
Bakken L. R., 1995, Nucleic acids in the environment., P9
[4]   Role of the soil matrix and minerals in protecting natural organic materials against biological attack [J].
Baldock, JA ;
Skjemstad, JO .
ORGANIC GEOCHEMISTRY, 2000, 31 (7-8) :697-710
[5]   Use of rhizosphere carbon sources in sole carbon source tests to discriminate soil microbial communities [J].
Campbell, CD ;
Grayston, SJ ;
Hirst, DJ .
JOURNAL OF MICROBIOLOGICAL METHODS, 1997, 30 (01) :33-41
[6]   CLASSIFICATION AND CHARACTERIZATION OF HETEROTROPHIC MICROBIAL COMMUNITIES ON THE BASIS OF PATTERNS OF COMMUNITY-LEVEL SOLE-CARBON-SOURCE UTILIZATION [J].
GARLAND, JL ;
MILLS, AL .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1991, 57 (08) :2351-2359
[7]   ANALYSIS OF FACTORS AFFECTING THE ACCURACY, REPRODUCIBILITY, AND INTERPRETATION OF MICROBIAL COMMUNITY CARBON SOURCE UTILIZATION PATTERNS [J].
HAACK, SK ;
GARCHOW, H ;
KLUG, MJ ;
FORNEY, LJ .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1995, 61 (04) :1458-1468
[8]  
Insam H, 1997, MICROBIAL COMMUNITIES, P259
[9]  
Insam H., 2004, MOL MICROBIAL ECOLOG
[10]   EFFECT OF SUBSTRATE LOCATION IN SOIL AND SOIL PORE-WATER REGIME ON CARBON TURNOVER [J].
KILLHAM, K ;
AMATO, M ;
LADD, JN .
SOIL BIOLOGY & BIOCHEMISTRY, 1993, 25 (01) :57-62