Industrial and mining activities have been named the major resources of soil rock contamination. distribution, and the entire ecological risk level ranged from low to moderate. This research also emphasized the need for partition in commercial and mining areas, the extensive application of spatial analysis methods, and the concern of human health risks in future studies. [4] analyzed ground contamination in the vicinity of the Dabaoshan Mine, Guangdong Province, China, and found that the environmental pollution in 20183-47-5 manufacture this area over the past decades has been caused by the 20183-47-5 manufacture contamination of a combination of Cu, Zn, Cd, and Pb. After further analysis, the authors predicted that this potential environmental risk caused by these metals would increase with time. Li [9] conducted a field survey to investigate the metal and As contamination levels in the ground and vegetables in four villages located along Baiyin, China and evaluated the possible health risks posed by such contamination to the local population through the food chain. The results revealed the most significantly contaminated ground in every village, the degree of contamination of vegetables in the four villages, and the environmental health risks assessed through breathing rate and food intake. Wang [10] analyzed the distribution of 10 heavy metals in the agricultural ground surrounding the worlds largest Rabbit Polyclonal to OMG Sb mine, located in China, and explored the degree and spatial distribution of the heavy metal pollution of the Sb mine-affected agricultural ground. The results showed large amounts of 10 heavy metals as well as integrated 20183-47-5 manufacture pollution indexes. Luo [11] investigated the metal pollution in the surrounding environment of an inoperative e-waste processing facility and found that the ground at former incineration sites experienced the highest concentrations of Cd, Cu, Pb, and Zn and that the uncontrolled e-waste processing operations caused serious pollution to the neighborhood veggie and garden soil items. The clearing up of former incineration sites ought to be a priority in virtually any future remediation program hence. Zhao [12] looked into heavy metal contaminants close to the Dabaoshan mine and discovered that the common concentrations of Cu, Zn, Compact disc, and Pb in the garden soil in the analysis region are above the organic garden soil history amounts, with Cd being the major pollutant that poses a human health risk. Fu and Wei [13] conducted a survey in an aged Sb mine in Xikuangshan, China, and found high concentrations of Hg and Cd, moderate concentrations of As, Pb, and Zn, and Cr concentrations comparable to the background values. The concentration of heavy metal contaminants in ground and the spatial variations of heavy metal contaminants have been the focus of previous studies. Comprehensive analysis methods have also been utilized in studies on ground heavy metal contamination. At present, the integrated pollution index is the most widely used method in many studies, such as that by Wang [10]. With Pollution-free vegetable production environment requirements (GB/T 18407.1-2001) [14] as basis for evaluation and by using the Nemerow index method, Xu and Ji [15] assessed the mean integrated heavy metal pollution index of the ground in Jiangsu province. Zhao [16] applied the geo-accumulation index (Igeo) and the pollution weight index to assess environmentally sensitive elements in Xining, China. Shi [17] evaluated heavy metal contamination levels using Igeo and potential ecological risk index (RI) values. Although spatial distribution and integrated heavy metal contamination have been extensively analyzed, current methods for the assessment 20183-47-5 manufacture of ground heavy metal contamination in China are typically simplex ones. A simplex spatial distribution analysis and separate extensive index methods usually do not successfully and accurately reveal earth heavy metal contaminants caused by.