This paper describes the model of heavy metal-Cu contaminated soil remediation standard value based on risk assessment. In the Cu contamination risk assessment model, the main exposure methods are oral ingestion and inhalation through breathing, which not only simplifies the calculation but also make people get a clearer understanding of the way of Cu contamination. We get the simplified formula, calculate and discuss Cu contaminated soil remediation target value in specific parameters to provide reference and basis for the remediation of Cu contaminated soil.

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In recent years, researchers have developed a number of new types of zero-valent nano-Fe remediation materials applied in the remediation of contaminated soil and water, which has attracted wide attentions. This paper selected soil leaching wastewater severely contaminated by chromium as target of the study and chose zero-valent nano-Fe, [Formula: see text] and [Formula: see text] for comparison experiments to study the effects on removing [Formula: see text] under experimental conditions of different pH values, dosages and reaction times. As is shown in the experiments, zero-valent nano-Fe has the highest removal rates for [Formula: see text], while the reaction of [Formula: see text] is the slowest under the same conditions. However, both removal rates are prone to be stable after 10 min. Dosages do not make a distinct difference and the pH value has the least effect on the repair of zero-valent nano-Fe.

Select the former site of a chemical factory in Chongqing, China as the typical Cr contaminated site. According to “Technical guidelines for risk assessment of contaminated sites” and “Standard of Soil Quality Assessment for Exhibition Sites (Interim)” (HJ-350-2007), this paper conducts health risk assessment for the site, and provide a basis for contaminated soil remediation. At the same time, according to the contaminated condition, used the Golden Software Surfer 8 to draw the boundary of contaminated soils and thus calculate the volume of contaminated soil. By estimation the volume is about 3122.3 m3, which provide detailed data for the later remediation engineering.

This paper is about the migration of the total petroleum hydrocarbon (TPH) contamination, which concludes the migration rule of the TPH contamination through designing indoor soil column leaching experiment. Through researching the migration concentration of different components of TPH, experiment concludes that different components have different relative transfer abilities in typical soil, and the transfer ability has an inverse relation to the molecular weight and the ring numbers of aromatic hydrocarbon. The purpose of this research is to provide guidance to nonproliferation and remediation of the petroleum contamination.