2017
DOI: 10.1016/j.ejsobi.2017.02.004
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Shift in soil microbial communities with shrub encroachment in Inner Mongolia grasslands, China

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Cited by 36 publications
(30 citation statements)
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“…These results contrast with previous studies which found the microbial biomass to be greater in soils beneath shrub canopies than adjacent grasses due to reduced environmental stress and greater stores of SOM (Gallardo and Schlesinger, 1992;Li et al, 2017;Ewing et al, 2007). As ratios between the fungal and bacterial constituents of the microbial 10 community share a negative relationship with soil pH (Bååth and Anderson, 2003), a decline in the fungal PLFA content of shrub soils can be attributed to changes in shrub soil pH which increased with gains in shrub cover (Table 1).…”
contrasting
confidence: 56%
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“…These results contrast with previous studies which found the microbial biomass to be greater in soils beneath shrub canopies than adjacent grasses due to reduced environmental stress and greater stores of SOM (Gallardo and Schlesinger, 1992;Li et al, 2017;Ewing et al, 2007). As ratios between the fungal and bacterial constituents of the microbial 10 community share a negative relationship with soil pH (Bååth and Anderson, 2003), a decline in the fungal PLFA content of shrub soils can be attributed to changes in shrub soil pH which increased with gains in shrub cover (Table 1).…”
contrasting
confidence: 56%
“…These plant community changes result in a structurally, physically and biologically different ecosystem which significantly alter the spatial distribution and fluxes of nutrients and the biogeochemical cycling within dryland landscapes, with implications for the ongoing process of land degradation (Eldridge et al, 2011;Michaelides 20 et al, 2012). Nitrogen (N), in particular, is the most significant limiting factor of primary production and decomposition processes in dryland systems after water (Gebauer and Ehleringer, 2000), yet there is currently limited understanding of how ecosystem transformations associated with land degradation changes the distribution, speciation and cycling of N (Browning et al, 2008), as well as the associated soil microbial biomass (Li et al, 2017). As drylands occupy ~40% of the Earth's land surface, changes in the nutrient distributions, patterns and cycling within degrading areas have important implications for 25 biogeochemical cycles at the global scale (Delgado-Baquerizo et al, 2013).…”
Section: Introductionmentioning
confidence: 99%
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“…The mean annual temperature (MAT) and mean annual precipitation (MAP) at the SEG sites ranged from 0.3°C to 4.9°C and 282 to 376 mm, respectively, in typical grasslands and from 1.8°C to 4.9°C and 200 to 285 mm, respectively, in desert grasslands (Table S1). Climatic data were obtained using interpolation methods based on original climate station data from 1975 to 2005 in Inner Mongolia (Li et al, ). During the period of this study, the vegetation of the study sites was dominated by the herbaceous species Leymus chinensis and Stipa krylovii .…”
Section: Methodsmentioning
confidence: 99%
“…Shrub encroachment typically leads to a transition in land cover from herb‐dominated grasslands to a mosaic landscape of shrub‐encroached grassland (SEG), in which shrub patches are interspersed within a grassy matrix (Chen et al, ). These vegetation changes can alter the quantities and qualities of aboveground and belowground residue inputs as well as the soil microbial community (Knapp et al, ; Li et al, ; Zhou, Boutton, & Wu, ), and can ultimately influence the cycling of carbon (C) and nitrogen (N) in grassland ecosystems (Don, Schumacher, & Freibauer, ; Guo & Gifford, ; Throop & Archer, ).…”
Section: Introductionmentioning
confidence: 99%