Accelerated soil formation due to paddy management on marshlands (Zhejiang Province, China)

被引:86
作者
Koelbl, A. [1 ]
Schad, P. [1 ]
Jahn, R. [2 ]
Amelung, W. [3 ]
Bannert, A. [4 ]
Cao, Z. H. [5 ]
Fiedler, S. [6 ]
Kalbitz, K. [7 ]
Lehndorff, E. [3 ]
Mueller-Niggemann, C. [8 ]
Schloter, M. [4 ]
Schwark, L.
Vogelsang, V. [2 ,6 ]
Wissing, L. [1 ]
Koegel-Knabner, I. [1 ,9 ]
机构
[1] Tech Univ Munich, Dept Ecol & Ecosyst Management, Lehrstuhl Bodenkunde, Ctr Life & Food Sci Weihenstephan, D-85350 Freising Weihenstephan, Germany
[2] Univ Halle Wittenberg, Inst Agr & Nutr Sci, Prof Bodenkunde & Bodenschutz, D-06120 Halle, Germany
[3] Univ Bonn, Inst Crop Sci & Resource Conservat INRES, D-53115 Bonn, Germany
[4] Helmholtz Zentrum Munchen, Res Unit Environm Genom, D-85758 Oberschleissheim, Germany
[5] Chinese Acad Sci, Inst Soil Sci, Nanjing 210008, Jiangsu, Peoples R China
[6] Johannes Gutenberg Univ Mainz, Dept Geog, D-55099 Mainz, Germany
[7] Univ Amsterdam, Inst Biodivers & Ecosyst Dynam, NL-1090 GE Amsterdam, Netherlands
[8] Univ Kiel, Inst Geosci, D-24118 Kiel, Germany
[9] Tech Univ Munich, Inst Adv Study, D-85748 Garching, Germany
关键词
Phases of pedogenesis; Paddy soils; Soil organic matter; Soil mineralogy; Lipid biomarker; Decalcification; YANGTZE-RIVER ESTUARY; ORGANIC-MATTER; CARBON ACCUMULATION; SURFACE SEDIMENTS; RICE FIELDS; HYDROCARBONS; NITROGEN; WATER; FIXATION; RATIOS;
D O I
10.1016/j.geoderma.2013.09.005
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Inundation of paddy soils for submerged rice production strongly impacts soil formation. Here we used chronosequences with up to 2000 years of cultivation history to compare soil formation in non-inundated (non-paddy) cropping systems with the formation of soils used for paddy rice production. This approach allowed us to identify the influence of agricultural management at different stages of pedogenesis. Soil samples were taken from two chronosequences derived from uniform parent material in the coastal region of the Zhejiang Province (P.R. China). One chronosequence consisted of paddy soils of different ages (50-2000 years), characterized by a yearly cropping sequence of rice cultivation under flooded conditions alternated with a non-inundated crop. The adjacent non-inundated (non-paddy) chronosequence was exclusively used for non-inundated crop production for 50-700 years. Lipid biomarkers revealed origin and homogeneity of the original coastal sediments and enabled the reconstruction of a consistent land use history for both chronosequences. The chronological development of soil properties and horizons suggested that the formation of paddy soils can be subdivided into three phases. The initial phase of paddy soil development takes only a few decades and is dominated by desalinization and formation of a compacted plow pan, leading from Fluvisols to Anthraquic Cambisols. During the next centuries (second phase), the differentiation between paddy and non-paddy management becomes increasingly obvious in terms of accelerated carbonate losses and constantly increasing organic carbon concentrations in paddy topsoils. In the third stage of paddy soil development (>= 700 years), a (trans-)formation and redistribution of oxides is accompanied by clearly visible hydromorphic patterns in paddy subsoils, thus promoting further development from Cambisols to Hydragric Anthrosols. To account for the underlying processes we suggest modifying the depth and mottling criteria for the definitions of anthraquic and hydragric soil horizons in the classification of the World Reference Base for Soil Resources. The non-paddy chronosequence was characterized by a low degree of soil development in which decalcification-related processes dominated throughout 700 years of soil formation. Hence, soil formation under paddy management was accelerated relative to that under dryland cropping, even though the 2000-year-old paddy soils lacked evidence of an advanced stage of silicate weathering, formation of pedogenic clay minerals, or clay migration. (C) 2013 Elsevier B.V. All rights reserved.
引用
收藏
页码:67 / 89
页数:23
相关论文
共 67 条
[1]  
Ahmad D., 1993, Pertanika Journal of Science & Technology, V1, P93
[2]   COMBINING BIOMARKER WITH STABLE ISOTOPE ANALYSES FOR ASSESSING THE TRANSFORMATION AND TURNOVER OF SOIL ORGANIC MATTER [J].
Amelung, W. ;
Brodowski, S. ;
Sandhage-Hofmann, A. ;
Bol, R. .
ADVANCES IN AGRONOMY, VOL 100, 2008, 100 :155-250
[3]   RATIOS OF MICROBIAL BIOMASS CARBON TO TOTAL ORGANIC-CARBON IN ARABLE SOILS [J].
ANDERSON, TH ;
DOMSCH, KH .
SOIL BIOLOGY & BIOCHEMISTRY, 1989, 21 (04) :471-479
[4]  
[Anonymous], 1986, ADV SOIL SCI
[5]  
ASHLEY GM, 1973, J SEDIMENT PETROL, V43, P298
[6]   Changes in Diversity and Functional Gene Abundances of Microbial Communities Involved in Nitrogen Fixation, Nitrification, and Denitrification in a Tidal Wetland versus Paddy Soils Cultivated for Different Time Periods [J].
Bannert, Andrea ;
Kleineidam, Kristina ;
Wissing, Livia ;
Mueller-Niggemann, Cornelia ;
Vogelsang, Vanessa ;
Welzl, Gerhard ;
Cao, Zhihong ;
Schloter, Michael .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 2011, 77 (17) :6109-6116
[7]   The contribution of agricultural and urban activities to inorganic carbon fluxes within temperate watersheds [J].
Barnes, Rebecca T. ;
Raymond, Peter A. .
CHEMICAL GEOLOGY, 2009, 266 (3-4) :318-327
[8]  
Blake G.R., 1986, METHODS SOIL ANAL SS
[9]  
Blakemore LC, 1987, METHODS CHEM ANAL SO, V80
[10]   Hydrocarbons in surface Sediments from the Changjiang (Yangtze River) Estuary, East China Sea [J].
Bouloubassi, I ;
Fillaux, J ;
Saliot, A .
MARINE POLLUTION BULLETIN, 2001, 42 (12) :1335-1346