Variational analysis MCv by R. Tyrrell Rockafellar, Roger J.-B. Wets, Maria Wets

By R. Tyrrell Rockafellar, Roger J.-B. Wets, Maria Wets

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31 4 Summary and Status of Whole Sediment TIEs . . . . . . . . . . . . . . . . . . . . . . 35 References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36 1 Background There are billions of tons of contaminated sediments in the streams, rivers, ponds, lakes, estuaries, and coastal areas of the world’s aquatic environments. , seafood), and serve as a source of bioaccumulable contaminants which transfer throughout aquatic and terrestrial food webs [1, 2].

Pesticides) were responsible for the observed toxic effects. In the final part of the TIE, Phase III, the results of the first two phases are confirmed. Generally, independent methods are used to perform the confirmation. By the 1990s and early 2000s, the focus of TIE methods development was on their use with contaminated sediments [8–10]. Ho and Burgess [11] provide an overview of interstitial water and whole sediment TIE methods; consequently, only a brief review is presented here. Contaminated sediment TIE methods evolved initially from the earlier effluent and receiving water methods with the TIEs performed on sediment interstitial waters [8–10, 12].

In the final part of the TIE, Phase III, the results of the first two phases are confirmed. Generally, independent methods are used to perform the confirmation. By the 1990s and early 2000s, the focus of TIE methods development was on their use with contaminated sediments [8–10]. Ho and Burgess [11] provide an overview of interstitial water and whole sediment TIE methods; consequently, only a brief review is presented here. Contaminated sediment TIE methods evolved initially from the earlier effluent and receiving water methods with the TIEs performed on sediment interstitial waters [8–10, 12].

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