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Effects of Wetland Utilization Change on Spatial Distribution of Soil Nematodes in Heihe River Basin, Northwest China

Effects of Wetland Utilization Change on Spatial Distribution of Soil Nematodes in Heihe River Basin, Northwest China
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摘要 The first account of the effects of wetland reclamation on soil nematode assemblages were provided, three sites in Heihe River Basin of Northwest China, that is grass wetland(GW), Tamarix chinensis wetland(TW) and crop wetland(CW) treatments, were compared. Results showed that the majority of soil nematodes were presented in the 0–20 cm soil layers in CW treatments, followed by in the 20–40 cm and 40–60 cm layers in GW treatments. Plant-feeding nametodes were the most abundant trophic groups in each treatment, where GW(91.0%) > TW(88.1%) > CW(53.5%). Generic richness(GR) was lower in the TW(16) than that in GW(23) and CW(25). The combination of enrichment index(EI) and structure index(SI) showed that the soil food web in GW was more structured, and those in TW was stressed, while the enrichment soil food web was presented in the CW treatment. Several ecological indices which reflected soil community structure, diversity, Shannon-Weaver diversity(H′), Evenness(J′), Richness(GR) and modified maturity index(MMI) were found to be effective for assessing the response of soil namatode communities to soil of saline wetland reclamation. Furthermore, saline wetland reclamation also exerted great influence on the soil physical and chemical properties(p H, Electric conductivity(EC), Total organic carbon(TOC), Total nitrogen(Total-N) and Nitrate Nitrogen(N-NO3–)). These results indicated that the wetland reclamation had significantly effects on soil nematode community structure and soil properties in this study. The first account of the effects of wetland reclamation on soil nematode assemblages were provided, three sites in Heihe River Basin of Northwest China, that is grass wetland(GW), Tamarix chinensis wetland(TW) and crop wetland(CW) treatments, were compared. Results showed that the majority of soil nematodes were presented in the 0–20 cm soil layers in CW treatments, followed by in the 20–40 cm and 40–60 cm layers in GW treatments. Plant-feeding nametodes were the most abundant trophic groups in each treatment, where GW(91.0%) 〉 TW(88.1%) 〉 CW(53.5%). Generic richness(GR) was lower in the TW(16) than that in GW(23) and CW(25). The combination of enrichment index(EI) and structure index(SI) showed that the soil food web in GW was more structured, and those in TW was stressed, while the enrichment soil food web was presented in the CW treatment. Several ecological indices which reflected soil community structure, diversity, Shannon-Weaver diversity(H′), Evenness(J′), Richness(GR) and modified maturity index(MMI) were found to be effective for assessing the response of soil namatode communities to soil of saline wetland reclamation. Furthermore, saline wetland reclamation also exerted great influence on the soil physical and chemical properties(p H, Electric conductivity(EC), Total organic carbon(TOC), Total nitrogen(Total-N) and Nitrate Nitrogen(N-NO3–)). These results indicated that the wetland reclamation had significantly effects on soil nematode community structure and soil properties in this study.
出处 《Chinese Geographical Science》 SCIE CSCD 2016年第3期339-351,共13页 中国地理科学(英文版)
基金 Under the auspices of Major State Basic Research Development Program of China(No.2009CB421302) National Natural Science Foundation of China(No.30670375,41201245)
关键词 土壤线虫 湿地利用 黑河流域 空间分布 湿地开垦 物理化学性质 线虫群落 群落结构 soil nematode spatial distribution community structure ecological index wetland exploration
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  • 1Bongers, T. and Bongers, M. 1998. Functional diversity of nematodes. Applied Soil Ecology. 10: 259-251.
  • 2Bongers, T. and Ferris, H. 1999. Nematode community structure as a bioindicator in environmental monitoring. Trends of Ecology and Evolution. 14: 224-228.
  • 3De Goede, R. G. M. and Bongers, T. 1994. Nematode community structure in relation to soil and vegetation characteristics. Applied Soil Ecology. 1: 29--44.
  • 4Ekschmitt, K., Bakonyi, G., Bongers, M., Bonggers, T., Bostrom, S., Dogan, H., Harrison, A., Nagy, P., O'Donell, A. G., Papatheodoru, E. M., Sohlenius, B., Stamou, G. P. and Wolters, V. 2001. Nematode community structure as indicator of soil functioning in European grassland soils. European Journal of Soil Biology. 37: 263-268.
  • 5Feng, M. Y., Yang, Z., Deng, Y. L. and He, J. F. 2003. Grassland rehabilitation and social development in the low mountain area of the Jinsha River Valley, China. Mountain Research and Development. 23: 124-127.
  • 6Ferris, H., Bongers, T. and de Goede, R. G. M. 2001. A framework for soil food web diagnostics: extension of the nematode faunal analysis concept. Applied Soil Ecology. 18: 13-29.
  • 7Gao, J. L., Terefework, Z., Chen, W. X. and Lindstrom, K. 2001. Genetic diversity of rhizobia isolated from Astragalus adsurgens growing in different geographical regions of China. Journal of Biotechnology. 91: 155-168.
  • 8Jiang, D. M., Liu, Z. M., Cao, C. Y., Kou, Z. W. and Wang, R. Y. 2003. Desertification and Ecological Restoration of Horqin Sandy Land (in Chinese). China Environmental Science Press, Beijing. pp 357-366.
  • 9Kandji, S. T., Ogol, C. K. P. O. and Albrecht, A. 2001. Diversity of plant-parasitic nematodes and their relationships with some soil physico-chemical characteristics in improved fallows in western Kenya. Applied Soll Ecology. 18: 143-157.
  • 10Li, S. G., Harazono, Y., Oikawa, T, Zhao, H. L., He, Z. Y. and Chang, X. L. 2000. Grassland desertification by grazing and the resulting micrometeorological changes in Inner Mongolia. Agricultural and Forest Meteorology. 102: 125-137.

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