Carbon and nitrogen distribution in water-stable aggregates under two tillage techniques in Fluvisols of Owerri area, southeastern Nigeria

被引:55
作者
Onweremadu, E. U. [2 ]
Onyia, V. N. [3 ]
Anikwe, M. A. N. [1 ]
机构
[1] Enugu State Univ Sci & Technol, Dept Agr & Econ Management, Enugu, Nigeria
[2] Fed Univ Technol Owerri, Dept Soil Sci & Technol, Owerri, Nigeria
[3] Fed Univ Technol Owerri, Dept Crop Sci & Technol, Owerri, Nigeria
关键词
soil aggregation; floodplain; long-term experiment; intercropping system; tropical environment;
D O I
10.1016/j.still.2007.09.011
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Organic matter influences soil structure and compactibility by binding soil mineral particles, reducing aggregate wettability, and influencing the mechanical strength of soil aggregates, which is the measure of coherence of inter-particle bonds. This work was carried out to examine how differences in water-stable aggregates influence the distribution of soil organic carbon and soil organic nitrogen under two tillage techniques [minimum tillage (only planting holes were opened) and conventional tillage (raised beds, 30 cm high, prepared manually with traditional hoes)] in soils of a Fluvisol in Owerri, southeastern Nigeria. Three pedons were dug and studied for each of the tillage technique along a soil sequence. Soil organic carbon and soil organic nitrogen distribution in whole soil and in water-stable aggregates under minimum tillage and conventional tillage were determined for the soils. Soil organic carbon contents in water-stable aggregates (WSA) of the pedons varied according to method of tillage. The highest mean values of soil organic carbon were obtained from minimum tillage and in water-stable aggregates 4.75-2.00 mm (16.03 Mg C ha(-1)), 1.00-0.50 mm (14.06 Mg C ha(-1)) and water-stable aggregates 2.00-1.00 mm (13.99 Mg C ha(-1)) whereas under conventional tillage, water-stable aggregates 1.00-0.50 mm with soil organic carbon of 24.6 Mg C ha(-1) had the highest soil organic carbon content. Soil organic carbon correlated significantly with mean weight diameter (r = 0.48; P = 0.05; n = 15), water-stable aggregates 4.75-2.00 mm (r = 0.73; P = 0.05; n = 15), water-stable aggregates 2.00-1.00 mm (r = 0.55; P = 0.05, n = 15), water-stable aggregates 1.00-0.50 mm (r = 0.44; P = 0.05; n = 15) whereas no relationship was found between soil organic carbon and water-stable aggregates 0.50-0.25 mm (r = 0.15; P = 0.05; n = 15) and water-stable aggregates <0.25 mm (r = 0.17; P = 0.05; n = 15) in soils under minimum tillage. There was a significant correlation (r = 0.45-0.58; P = 0.05; n = 14) between all water-stable aggregates classes studied and soil organic carbon in soils under conventional tillage. Mean values of soil organic nitrogen were higher in soils under minimum tillage with 4.75-2.00 mm and 2.00-1.00 mm aggregate classes having 1.64 Mg N ha(-1) and 1.57 Mg N ha(-1) soil organic nitrogen when compared to 1.01 Mg N ha(-1) and 1.00 Mg N ha(-1) in conventionally tilled soils of the same aggregate classes, respectively. Larger water-stable aggregate classes (4.75-2.00; 2.00-1.00) had slightly more soil organic nitrogen (22-26%) than smaller aggregate classes (1.00-0.50; 0.50-0.25; >0.25) with 14-24% soil organic nitrogen in minimum tilled soils. In soils under conventional tillage, 1.00-0.50 mm, 0.50-0.25 mm and <0.25 mm aggregate classes contributed more soil organic nitrogen (19.66-22.40%) to the soil whereas larger water-stable aggregate classes contributed 19.22% soil organic nitrogen. The proportion of soil organic carbon and total nitrogen retained in soils with higher percentage of water-stable aggregates are less likely to be lost through soil and wind erosion. The higher values of SOC in the whole soil and WSA classes less than 2.00 mm are indications of positive influence of SOC on the stability of these peds. (C) 2007 Elsevier B.V. All rights reserved.
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页码:195 / 206
页数:12
相关论文
共 43 条
[1]  
[Anonymous], 1998, WORLD REF BAS SOIL R
[2]  
[Anonymous], POLISH J SOIL SCI
[3]  
Bremner J.M., 1996, Nitrogen-total. Methods of soil analysis. Part, P1085
[4]   CARBON TURNOVER IN SOIL PHYSICAL FRACTIONS [J].
BUYANONOVSKY, GA ;
ASLAM, M ;
WAGNER, GH .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1994, 58 (04) :1167-1173
[5]   CARBON AND NITROGEN DISTRIBUTION IN AGGREGATES FROM CULTIVATED AND NATIVE GRASSLAND SOILS [J].
CAMBARDELLA, CA ;
ELLIOTT, ET .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1993, 57 (04) :1071-1076
[6]   Soil quality for sustainable land management: Organic matter and aggregation interactions that maintain soil functions [J].
Carter, MR .
AGRONOMY JOURNAL, 2002, 94 (01) :38-47
[7]  
Castro Filho C., 1998, Revista Brasileira de Ciencia do Solo, V22, P527, DOI 10.1590/S0100-06831998000300019
[8]  
Castro Filho C., 2002, Soil and Tillage Research, V65, P45, DOI 10.1016/S0167-1987(01)00275-6
[9]  
Cheshire MV, 1996, BIOL FERT SOILS, V21, P166, DOI 10.1007/BF00335929
[10]  
COCHRANE HR, 1994, P 3 TRIENN C SOILS 9, P207