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Dissolution Kinetics of Heavy Metals in Dutch Carbonate- and Sulfide-Rich Freshwater Sediments

S. E. J. Buykx*,a, M. A. G. T. van den Hoopa and J. P. G. Lochb

a National Institute of Public Health and the Environment, P.O. Box 1, 3720 BA Bilthoven, the Netherlands
b Department of Geochemistry, Institute of Earth Sciences, Utrecht University, P.O. Box 80021, 3508 TA Utrecht, the Netherlands



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Fig. 1. pH vs. extraction time at different added HCl concentrations, after a one-time addition of HCl. Method 1: (a) Kromme Rijn, (b) Biesbosch. Dotted lines are duplicates.

 


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Fig. 2. pH vs. extraction time at different added HCl concentrations, with intermittent HCl additions during the first 1000 min. Method 2: (a) Kromme Rijn, (b) Biesbosch. Dotted lines are duplicates. For 0.60 mol L-1 the acid was added in 110 and 250 min, respectively, instead of in 1000 min.

 


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Fig. 3. Extracted metal concentrations vs. final pH, Kromme Rijn sediment ({blacktriangleup} = 24-h extraction, x = 45-min extraction, dry wt. = dry weight)

 


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Fig. 4. Extracted metals vs. final pH, Kromme Rijn compared with Biesbosch for the 45-min extraction ({square} = Kromme Rijn, {diamondsuit} = Biesbosch)

 


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Fig. 5. Acid volatile sulfide (AVS) vs. pH for the 45-min extraction time ({square} = Kromme Rijn, {diamondsuit} = Biesbosch)

 


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Fig. 6. Simultaneously extracted metals (SEM) to acid volatile sulfide (AVS) ratio vs. pH for the 45-min extraction time ({square} = Kromme Rijn, {diamondsuit} = Biesbosch)

 





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