Abstract

Food security and cultivated land utilization can be seriously affected by heavy metal (HM) pollution of the soil. Therefore, identifying the pollution sources of farmland is the way to control soil pollution and enhance soil quality effectively. In this research, 95 surface soil samples, 34 vegetable samples, 27 irrigation water samples, and 20 fertilizer samples were collected from the Wuqing District of Tianjin City, China and was used to determine their HMs accumulation and potential ecological risks. Then, kriging interpolation and positive matrix factorization (PMF) were utilized to identify the sources of soil HMs. The results indicated that soil HMs in the study area were contaminated at a medium level, but that the pollution of Cd was more severe, and the Cd content in vegetables was slightly higher than the permissible threshold (0.02 mg·kg−1). Furthermore, a non-homogeneous distribution was observed, with higher concentrations of HM contaminants concentrated in the southwest of the study area, where many metal manufacturing industries are located. Our results suggest that the Cd originated from industrial activity; As and Pb from agricultural practices; Ni, Cu, Cr, and As mainly from natural sources; Zn and Cu from organic fertilizer; Pb and Cd mainly from traffic discharge; and Cr, Ni, and Pb from sewage irrigation. Obviously, the accumulation of soil HMs in the study area could be mainly attributed to industrial activities, implying the need for implementation of government strategies to reduce industrial point-source pollution.

Highlights

  • Value a /Soils background values in Tianjin City (GB15618-2018).agricultural soils in China (GB15618-2018). bRisk Screening Values Rates (%) b /Exceedance 6.5 < pH ≤ 7.5 pH > 7.5 0.3 (6.25%)

  • A combination of kriging interpolation, and positive matrix factorization (PMF) modeling was used for source apportionment of heavy metal (HM) in topsoils from the Wuqing District

  • By comparing the relationship between total and available HMs in soil, it was found that the proportion of DTPA Cd, As, and Cu was higher

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Summary

Study Area

The study area is in Wuqing, northwestern Tianjin (116◦ 460 –117◦ 190 E, 39◦ 070 –39◦ 420 N), which is located in the lower part of the North China alluvial plain, with a gentle terrain and a total area of 1574 km. The region features a temperate continental monsoon climate, with an annual average temperature of 11.6 ◦ C, and an annual rainfall of 500–610 mm. The area has many industrial parks, including industry, material manufacturing, automobile parts industry, and steel industry. It is one of the main vegetable production areas in Tianjin city. The characteristics of HM pollution sources in farmland are complex, seriously threatening the sustainable use of regional agricultural resources and the safety of agricultural products

Data Acquisition
Soil and Vegetable
Collection of Irrigation Water and Organic Fertilizer
Analytical Method
Evaluation of HMs Pollution in Soil
Ecological Risk Assessment of HMs in Soil
Bioconcentration Factor
Positive Matrix Factorization Model
Statistical and Geostatistical Analysis
Accumulation of HMs in Soil
Background
Bioavailability of HMs in Soil
Spatial Distribution of Soil Metals
Accumulation of HMs in Vegetables
Source
Source Identification of Metals in Soils
Conclusions
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