Abstract:A level III fugacity model was applied to characterize the fate of gamma-HCH in Tianjin, China, before the 1990s when the contamination reached its maximum at steady state. Geometric means were used as model inputs. The concentrations of gamma-HCH in air, surface water, soil, sediment, crops, and fish as well as transfer fluxes across the interface between the compartments were derived under the assumption of steady state. The calculated concentrations were validated by independent data collected from the lite… Show more
“…Compared with other countries, the levels for most of the rivers in China were also found to have TCS concentrations in sediment more than 3 ng/g. When compared to the available reported concentrations in Chinese rivers, the differences between the PECs and MECs mostly fell within an acceptable range (less than a log-unit range) (Cao et al 2004;Liu et al 1999) (Table 4). The more measured concentrations from a river, the more representative the average value, especially for the large rivers.…”
Section: Prediction Of Tcs Concentrations In Each Basinmentioning
confidence: 90%
“…Combining the chemical usage data, population, removal rate in WWTPs and a parameterized multimedia model describing the fate of chemicals, the chemical concentrations in the environment can be predicted, and it has been proved to be effective and accurate (Keller et al 2007;Price et al 2009Price et al , 2010aWhelan et al 2012;Zhang et al 2013). Multimedia fugacity models are well established, well documented and widely used for predicting the environmental fate of different chemicals at various scales (single river scale, regional scale and global scale) (Cao et al 2004;Mackay and Paterson 1991;Prevedouros et al 2004;Tan et al 2007;Tao et al 2003;Wang et al 2012). We have successfully modelled environmental fate for TCS in Dongjiang River basin ) and for seven steroids in whole China .…”
This study aimed to investigate the emission and multimedia fate as well as potential risks of triclosan (TCS) in all of 58 basins in China. The results showed that the total usage of TCS in whole China was 100 t/year, and the discharge to the receiving environment was estimated to be 66.1 t/year. The predicted TCS concentrations by the level III fugacity model were within an order of magnitude of the reported measured concentrations. TCS (90.8 %) was discharged into the water compartment and 9.2 % to the soil compartment. The TCS concentration levels in east China were found generally higher than in west China. In addition, the input flux for TCS to seawater was largely attributed to the seasonal variations in advection flows. Preliminary risk assessment showed that medium to high ecological risks for TCS would be expected in the eastern part of China due to the high population density.
“…Compared with other countries, the levels for most of the rivers in China were also found to have TCS concentrations in sediment more than 3 ng/g. When compared to the available reported concentrations in Chinese rivers, the differences between the PECs and MECs mostly fell within an acceptable range (less than a log-unit range) (Cao et al 2004;Liu et al 1999) (Table 4). The more measured concentrations from a river, the more representative the average value, especially for the large rivers.…”
Section: Prediction Of Tcs Concentrations In Each Basinmentioning
confidence: 90%
“…Combining the chemical usage data, population, removal rate in WWTPs and a parameterized multimedia model describing the fate of chemicals, the chemical concentrations in the environment can be predicted, and it has been proved to be effective and accurate (Keller et al 2007;Price et al 2009Price et al , 2010aWhelan et al 2012;Zhang et al 2013). Multimedia fugacity models are well established, well documented and widely used for predicting the environmental fate of different chemicals at various scales (single river scale, regional scale and global scale) (Cao et al 2004;Mackay and Paterson 1991;Prevedouros et al 2004;Tan et al 2007;Tao et al 2003;Wang et al 2012). We have successfully modelled environmental fate for TCS in Dongjiang River basin ) and for seven steroids in whole China .…”
This study aimed to investigate the emission and multimedia fate as well as potential risks of triclosan (TCS) in all of 58 basins in China. The results showed that the total usage of TCS in whole China was 100 t/year, and the discharge to the receiving environment was estimated to be 66.1 t/year. The predicted TCS concentrations by the level III fugacity model were within an order of magnitude of the reported measured concentrations. TCS (90.8 %) was discharged into the water compartment and 9.2 % to the soil compartment. The TCS concentration levels in east China were found generally higher than in west China. In addition, the input flux for TCS to seawater was largely attributed to the seasonal variations in advection flows. Preliminary risk assessment showed that medium to high ecological risks for TCS would be expected in the eastern part of China due to the high population density.
“…Large amounts of OCPs such as HCHs and dichlorodiphenyltrichloroethane (DDT) have also been historically produced at many chemical plants in this region. The wastewater from these factories was also discharged into adjacent rivers and has contributed large quantities of pesticides to the local loadings (Cao et al 2004). Although the production of PCP and these pesticides has been banned for decades, due to their high stability and resistance to microbial degradation, these pollutants can persist in aquatic sediments for decades and may still pose an ecological risk.…”
The concentrations of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), dioxin-like polychlorinated biphenyls (dl-PCBs), and organochlorine pesticides (OCPs) in surface sediments from the lower reaches of the Haihe River basin, northern China, were determined by high-resolution gas chromatograph-high-resolution mass spectrometer. The concentrations of 2,3,7,8-substituted PCDD/Fs, dl-PCBs, and total OCPs [sum of hexachlorobenzene, hexachlorocyclohexanes, and dichlorodiphenyltrichloroethane (DDTs)] in 17 sediment samples were in the ranges of 11.6-1,180,924 pg/g dry weight (dw), 18.7-50,017 pg/g dw, and 1.7-35,280 ng/g dw, respectively. The contamination levels in the samples varied significantly between the different sites. Abnormally high concentrations of PCDD/Fs, dl-PCBs, and some OCPs were found in sediments from the lower reaches of the main channel of the Haihe River and the Dagu Drainage River, which were attributed to the historical production of pentachlorophenol and other pesticides near these locations. High levels of DDTs were detected in the Yongding New River sediment, which were likely to have originated from the discharge of wastewater from a dicofol factory upstream. In samples taken from other sites, the concentrations of these pollutants were at levels comparable to those documented in other areas of China. This preliminary investigation suggests that historical pesticide production in the Haihe River basin has contributed significantly to the contamination of this aquatic ecosystem and that further attention to this issue is warranted.
“…It is concluded that a steady state could be reached with the constant input of chemicals, and that the modeling parameters that we collected within a year are reasonable. Based on the approaches of Mackay and Paterson 22 and Cao et al 40 a level III fugacity model was developed to describe the partitioning, reaction, and diffusive and non-diffusive transfer processes of TCS and TCC in the Dongjiang River basin as well as its different sections (upstream, midstream, downstream, delta). As the steady state fugacity model assumed, each study area in this study is completely mixed.…”
“…23,45,46 In the analysis, probability distributions for input parameters were used to replace discrete values, by randomly selecting values from each input parameter distribution. 40 Through the Monte Carlo simulation method, the model ran 20 000 times and an output distribution of concentrations and transfer uxes in different environmental media were constructed. As the input parameters were assumed to have normal or log-normal distributions around the mean or point value (Fig.…”
Section: This Journal Is ª the Royal Society Of Chemistry 2013mentioning
Triclosan (TCS) and triclocarban (TCC) are two active ingredients widely used in many home and personal care products. Multimedia fate of TCS and TCC in the Dongjiang River basin, South China were addressed by the developed level III fugacity model based on their usage. Under the assumption of steady state, the concentrations in air, water, soil, sediment, suspended particulate matter (SPM) and fish as well as transfer flux across the interface between the compartments were simulated. The measured concentrations for the two compounds in water, SPM, and sediment from field monitoring campaigns were then compared to validate the model. The results showed that the model predicted reasonably accurate concentrations and the differences between the measured and modeled concentrations were all less than 0.7 log units. TCS and TCC had a tendency to distribute into the sediment phase, which accounted for more than 66.3% and 90.3% of the total masses, respectively. Wastewater discharge was the main source for the occurrence of the two compounds in the aquatic environment, while degradation was the primary process for the loss in the study area, followed by the advection export.Sensitivity analysis showed that the most influential parameters for the fate of the target chemicals were source term, degradation rates and adsorption coefficients. Monte Carlo simulation could well describe the modeling uncertainty and variability.
Environmental impactPersonal care products are widely used in everyday life. Aer use, they are discharged into the receiving environments directly or indirectly. Their detection in the environment has become an increasing concern due to their potential impacts on the ecosystem. This paper developed a modied level III fugacity model to assess the multimedia fate of two personal care products (triclosan and triclocarban) in a river basin based on their usage data and evaluated the model by eld monitoring data in the Dongjiang River Basin. The modied steady state fugacity model can be used to evaluate contamination of personal care products at the basin scale based on their usage. This tool could be adopted by various decision-makers in the management of chemicals in river basins.
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