Sorption of micropollutants to natural aquatic particles = Sorptie van microverontreinigingen aan natuurlijke aquatische deeltjes
Sorption to natural aquatic particles plays an important role in the bioavailability and fate of micropollutants. The characteristics of sorption were investigated for hydrophobic organic compounds (HOCs) and heavy metals using a wide variety of natural aquatic particles. Special attention was paid to (bio)sorption to phytoplankton and detritus. The extent of sorption can be quantified by a distribution- ( K d ) or partitioncoefficient ( K p ). It was shown in this study that such coefficients in aquatic systems are variable in space and time because:1. At more or less constant environmental conditions K d values for trace metals depend on the content of iron(hydr)oxides, manganese(hydr)oxides and organic matter in the natural aquatic particles. It was shown for Lake Volkerak/Zoom that this content varies considerably in time and space, and that K d values for cadmium differ up to factor 30 (field data) or a factor 300 (laboratory). For mineralizing planktonic particles in the laboratory, K d increases up to a factor 10 - 20 (lead) were observed under conditions similar to those in Lake Volkerak/Zoom.2. When K p values for HOCs are calculated with respect to an aqueous phase which contains organic matter, the apparent K p depends on the organic carbon fraction in the aqueous phase and the particle to water ratio. Further, K p depends on organic matter content and composition. It was shown for 1,2,3,4-tetrachlorobenzene that laboratory K p values varied a factor 30 for particles from lake Volkerak/Zoom. Organic matter content of suspended solids showed a strong seasonal variation. Normalization to organic carbon removes only a part of the variation. Comparison of carbon normalised HOC concentrations (field data) in settling solids with those in simultaneously sampled suspended solids showed a difference of a factor 2 - 6. Under controlled laboratory conditions, significant K oc differences between fresh phytoplankton cells, detritus and sediments were found.3. Hydrophobic sorption to suspended solids may not be at equilibrium in many aquatic systems. This is caused by retarded adsorption or desorption, or for phytoplankton by the combined action of retarded bioaccumulation and algal growth.
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| Format: | Doctoral thesis biblioteca |
| Language: | English |
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Landbouwuniversiteit Wageningen
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| Subjects: | adsorption, aquatic environment, canals, geological sedimentation, plankton, rivers, sorption, streams, surface water, water, water pollution, water quality, adsorptie, aquatisch milieu, geologische sedimentatie, kanalen, oppervlaktewater, rivieren, sorptie, waterkwaliteit, waterlopen, waterverontreiniging, |
| Online Access: | https://research.wur.nl/en/publications/sorption-of-micropollutants-to-natural-aquatic-particles-sorptie- |
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| Summary: | Sorption to natural aquatic particles plays an important role in the bioavailability and fate of micropollutants. The characteristics of sorption were investigated for hydrophobic organic compounds (HOCs) and heavy metals using a wide variety of natural aquatic particles. Special attention was paid to (bio)sorption to phytoplankton and detritus. The extent of sorption can be quantified by a distribution- ( K d ) or partitioncoefficient ( K p ). It was shown in this study that such coefficients in aquatic systems are variable in space and time because:1. At more or less constant environmental conditions K d values for trace metals depend on the content of iron(hydr)oxides, manganese(hydr)oxides and organic matter in the natural aquatic particles. It was shown for Lake Volkerak/Zoom that this content varies considerably in time and space, and that K d values for cadmium differ up to factor 30 (field data) or a factor 300 (laboratory). For mineralizing planktonic particles in the laboratory, K d increases up to a factor 10 - 20 (lead) were observed under conditions similar to those in Lake Volkerak/Zoom.2. When K p values for HOCs are calculated with respect to an aqueous phase which contains organic matter, the apparent K p depends on the organic carbon fraction in the aqueous phase and the particle to water ratio. Further, K p depends on organic matter content and composition. It was shown for 1,2,3,4-tetrachlorobenzene that laboratory K p values varied a factor 30 for particles from lake Volkerak/Zoom. Organic matter content of suspended solids showed a strong seasonal variation. Normalization to organic carbon removes only a part of the variation. Comparison of carbon normalised HOC concentrations (field data) in settling solids with those in simultaneously sampled suspended solids showed a difference of a factor 2 - 6. Under controlled laboratory conditions, significant K oc differences between fresh phytoplankton cells, detritus and sediments were found.3. Hydrophobic sorption to suspended solids may not be at equilibrium in many aquatic systems. This is caused by retarded adsorption or desorption, or for phytoplankton by the combined action of retarded bioaccumulation and algal growth. |
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