Li Gang

Li Gang


Research Focus & Metrics

Academic Career Length

10Years (2017-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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5 December 2019 in Environmental Earth Sciences
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Journal Article
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JXJiaxing Xu
Jiaxing Xu
HZHua Zhao
Hua Zhao
PYPengcheng Yin
Pengcheng Yin
LWLixin Wu
Lixin Wu
LGLi Gang
Li Gang

17 April 2017 in Sustainability
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JQJun-Feng Qu
Jun-Feng Qu
YHYu-Le Hou
Yu-Le Hou
MGMeng-Yu Ge
Meng-Yu Ge
KWKun Wang
Kun Wang
SLShu Liu
Shu Liu
FCFu Chen
Fu Chen
Soil organic carbon (SOC) plays an essential role in the early stages of pedogenisis and ecological restoration in reclaimed mine soils. Dynamic changes in the SOC content are essential for assessing the quality of reclaimed mine soils and the effect of ecological restoration. To objectively assess the carbon dynamics of reclaimed soils, we selected the surface (0–20 cm) soil of farmland under agricultural use (soybean–wheat rotation) from a reclamation chronosequence (R4: 4 years of reclamation, R7: 7 years of reclamation, R10: 10 years of reclamation and R13: 13 years of reclamation) in the Dongtan Mining Area, Shandong Province, China. The adjacent normal, unaffected farmland was used as a control (CK). The results showed that the SOC content gradually increased with the reclamation age until it reached 7.98 g·kg−1 for R13, which accounted for 76% of that of the CK. However, the total carbon contents of the reclaimed soils did not significantly differ from and even appeared higher than that of the CK. This is mainly because the inorganic carbon contents of the reclaimed soils ranged from 2.98 to 12.61 g·kg−1, all of which were significantly higher than the 0.87 g·kg−1 obtained for the CK. The microbial biomass carbon (MBC) content and the microbial quotient significantly increased with the reclamation age of the soil, and both parameters were markedly higher for R13 than for the CK. The dissolved organic carbon (DOC) content and its ratio to the SOC were significantly higher for R4–R13 than for the CK and DOC/SOC gradually decreased with the reclamation age. Both the reclamation age and the temperature had positive effects on the soil basal respiration (SBR). The SBR rate constantly increased with the reclamation age and was markedly higher at 25 °C than at 15 °C. The temperature sensitivity (Q10) of the SBR showed a clearly decreasing trend for the reclamation chronosequence, but its value remained higher for R13 than for the CK (2.37). The metabolic quotient constantly decreased with the reclamation age, which suggests that the survival pressure imposed on soil microbes by the soil environment gradually decreased. These results indicate that it takes a long time for organic carbon to accumulate in reclaimed mine soil and that rational agricultural use contributes to sustained improvement of the quality of reclaimed soil.

17 September 2019 in Polish Journal of Environmental Studies
Verified
Journal Article
Closed access
JXJiaxing Xu
Jiaxing Xu
HZHua Zhao
Hua Zhao
PYPengcheng Yin
Pengcheng Yin
NBNaishun Bu
Naishun Bu
LGLi Gang
Li Gang
Landscape pattern change (LPC) can provide comprehensive insight into the effects of mining activities on regional ecosystems. This paper examined the impact of coal mining on LPC of Peixian mining area, China. An analysis of LPC was conducted based on GIS-RS technology from 1994 to 2014. The influence of coal mining on the LPC was studied quantitatively from the perspective of life cycle. The following conclusions were drawn: 1) The LPC of the study area changed significantly during the study period. Landscape type index showed a rising trend in fluctuation, and landscape fractal characteristics tended to be simplified and regularized. 2) Landscape indices of cultivated land and waterlogged subsidence zones were highly correlated with annual coal production, and the correlation coefficients were -0.634, -0.748 and 0.991, respectively. 3) The abrupt changes of largest patch index (LPI) and aggregation index (AI) of cultivated land occurred in 1999 and 2001, respectively. The LPI of waterlogged subsidence zones had a sustained upward trend since 1995, but the AI had a significant rising trend in 1997-2006 and 2011-2013. These results could provide useful guidance on sustainable land use planning and restoring the damaged landscape for underground coal mining areas.