2000
DOI: 10.1016/s0883-2927(99)00107-9
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Hydrogeochemistry and transport of organic contaminants in an urban watershed of Chesapeake Bay (USA)

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Cited by 80 publications
(51 citation statements)
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“…Concentrations of DDTs in particulate phase were much higher than those in dissolved phase in the Yangtze River (Fig. 5b), which was agreeable to results of other studies (Foster et al 2000;Yang et al 2004). Furthermore, the concentrations of DDTs in particulate phase had an increasing tendency along the Yangtze River from upstream to downstream and the peak concentration was observed at the site Y10.…”
Section: Phase Distributionsupporting
confidence: 92%
See 1 more Smart Citation
“…Concentrations of DDTs in particulate phase were much higher than those in dissolved phase in the Yangtze River (Fig. 5b), which was agreeable to results of other studies (Foster et al 2000;Yang et al 2004). Furthermore, the concentrations of DDTs in particulate phase had an increasing tendency along the Yangtze River from upstream to downstream and the peak concentration was observed at the site Y10.…”
Section: Phase Distributionsupporting
confidence: 92%
“…It can be seen from Fig. 5a that HCHs mostly existed in dissolved phase, which was well documented (Foster et al 2000). Similar phenomenon could be observed for the distribution of HCHs in the Pearl River in south China according to Yang et al (2004).…”
Section: Phase Distributionsupporting
confidence: 83%
“…The contamination of receiving waters nearby urban areas has been well documented and attributed to the discharge of stormwater runoff via combined sewer overflows and industrial and municipal effluent (Golomb et al, 2001;Foster et al, 2000), as well as to atmospheric deposition (Brunciak et al, 2001;Offenberg and Baker, 1997;Simcik et al, 1997). The effect of the 'urban atmospheric plume' on chemical loadings has been documented for Chesapeake Bay (Offenberg and Baker, 1997), Lake Michigan (Simcik et al, 1997), New Jersey estuary (Brunciak et al, 2001;Du et al, 2009) and the Hudson River estuary (Totten et al, 2004).…”
Section: Urban Emissions and Urban-rural Gradientsmentioning
confidence: 99%
“…The hygienic threshold values for each PCB congener in drinking water is 100 ng/L, 4 but when investigating the transport properties in a water environment, detection limits below 1 ng/L are sometimes required. [5][6][7][8][9][10][11] The need to determine very low concentrations of PCBs in natural water and wastewater samples calls for large concentration enrichment factors before a final determination is possible. This can be accomplished by liquid-liquid extraction (LLE), such as in the US EPA Method 608.…”
Section: Introductionmentioning
confidence: 99%
“…This can be accomplished by liquid-liquid extraction (LLE), such as in the US EPA Method 608. 12 LLE has been applied to determine PCBs in snow and river water in a low ng/L range using 0.5 L samples, 5 but in some cases over 10 L sample is required when analyzing PCBs at the pg/L level, as in tidal rivers 6 and seawater. 7 An alternative way of extracting PCBs from water is solid-phase extraction (SPE), as described in the US EPA Method 525.…”
Section: Introductionmentioning
confidence: 99%