2011
DOI: 10.1016/j.envpol.2011.07.010
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Inputs of antifouling paint-derived dichlorodiphenyltrichloroethanes (DDTs) to a typical mariculture zone (South China): Potential impact on aquafarming environment

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Cited by 43 publications
(26 citation statements)
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“…Overall, DDT and its metabolites in surface sediments from Port Ningbo were dominated by its p,p'-isomer and metabolites (Fig. 2), which is consistent with the composition of DDT and its metabolites in antifouling paints (Wang et al, 2007;Yu et al, 2011). Biocides other than DDT, such as tributyltin, Diuron, and Irgarol 1051, at levels exceeding global sediment quality guidelines have also been detected in shipping and shipbuilding ports in South Korea (Kim et al, 2015).…”
Section: Discussionsupporting
confidence: 72%
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“…Overall, DDT and its metabolites in surface sediments from Port Ningbo were dominated by its p,p'-isomer and metabolites (Fig. 2), which is consistent with the composition of DDT and its metabolites in antifouling paints (Wang et al, 2007;Yu et al, 2011). Biocides other than DDT, such as tributyltin, Diuron, and Irgarol 1051, at levels exceeding global sediment quality guidelines have also been detected in shipping and shipbuilding ports in South Korea (Kim et al, 2015).…”
Section: Discussionsupporting
confidence: 72%
“…Pollution of DDT and its metabolites in port sediments has been shown to derive from ship antifouling paints (Wang et al, 2007, Yu et al, 2011. In Guangdong Province of China, two antifouling paints available in the Hailing Bay area contained 9893 and 39,715 mg of DDT kg −1 wet paint (Yu et al, 2011) and other 2 antifouling paints available in the Pearl River Delta were 520 and 2400 mg DDT kg −1 wet paint (Wang et al, 2007), respectively. Three antifouling paints from Hong Kong markets contained DDT at 0.15-9.7 mg kg −1 wet paint and 5 antifouling paints available in the Bailing Bay, China ranged from 0.21-0.54 mg DDT kg −1 wet paint (Yu et al, 2011).…”
Section: Discussionmentioning
confidence: 99%
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“…27,39 The concentration profiles of the target chemicals ( Figure 3) were consistent with the presence of new input sources in the area and the biodegradation pathways of DDT. 16,25,27 Briefly, the concentrations of p,p′-DDD, p,p′-DDE, p,p′-DDMU, o,p′-DDMU, p,p′-DDNU, and p,p′-DBP, metabolites of p,p′-DDT or o,p′-DDT, in overlying water all sharply decreased outward the sediment−water interface, indicating the sediment as a source of these chemicals. On the other hand, the profiles of overlying water p,p′-DDT and o,p′-DDT, initially present in input sources (i.e., antifouling paint residues), exhibited apparent decreasing trends toward the sediment−water interface.…”
Section: ■ Results and Discussionmentioning
confidence: 98%
“…In the present study, only seven sampling cells were used, with the midpoints representing distances at 0. 25 Laboratory testing demonstrated that stainless steel shields and GF/F membranes used in the passive sampling device did not sorb significant amounts of the target chemicals. 16 Detailed cleaning and preparation procedures for assembly of the sampling device are presented in Supporting Information Text S1.…”
Section: ■ Sampling Device Design and Configurationmentioning
confidence: 99%