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Phthalates and Nonylphenols in Roskilde Fjord

Phthalates and Nonylphenols in Roskilde Fjord

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200NPNPDEConcentration, ng/g d.m.150100500Depth, cm0 5 10 15 20 25Age, yTwentyFortySixty EightyFigure 22NP <strong>and</strong> NPDE <strong>in</strong> sediment coreFor NP <strong>and</strong> NPDE, a very different <strong>and</strong> <strong>in</strong>terest<strong>in</strong>g pattern is observed <strong>in</strong>Figure 22, which display two pronounced maxima occurr<strong>in</strong>g at depths of7 <strong>and</strong> 18 cm, respectively. These maxima co<strong>in</strong>cides approximately – butnot precisely - with those observed for DEHP <strong>and</strong> BBP. A probable explanationfor this observation may be a long-term variation <strong>in</strong> the consumptionof NPE, s<strong>in</strong>ce these by an agreement between the detergent <strong>in</strong>dustry<strong>and</strong> the environmental authorities has been phased out <strong>in</strong> 1989.For the variation with depth, another factor of significance is the new <strong>and</strong>more efficient WWTP, taken <strong>in</strong>to operation <strong>in</strong> 1995. The current efficiencyis described by Fauser et al. (2000).For a more complete underst<strong>and</strong><strong>in</strong>g of the variation with depth, a modeltak<strong>in</strong>g care of the transport, adsorption <strong>and</strong> desorption as well as degradationwill be described <strong>in</strong> section 6.1.4. The model treats only the fateof DEHP, be<strong>in</strong>g the most abundant substance.5.3 Streams <strong>and</strong> lake5.3.1 WaterIn Table 17 the abundances of the substances <strong>in</strong> the stream <strong>and</strong> the lakewater are shown as mean <strong>and</strong> st<strong>and</strong>ard deviation of all samples45

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