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  Journal > Kluwer Publishers - Table of Contents > Volume 5 Issue 4 > Abstract
 


A field investigation of the relationship between zinc and acid volatile sulfide concentrations in freshwater sediments

Gerald T. Ankley1, Karsten Liber2, Daniel J. Call2, Thomas P. Markee2,
Timothy J. Canfield3 & Christopher G. Ingersoll3

1Mid-continent Ecology Division, U.S. Environmental Protection Agency,
6201 Congdon Boulevard, Duluth,Minnesota 55804, USA
2Lake Superior Research Institute, University of Wisconsin-Superior,
1800 Grand Avenue, Superior, Wisconsin54880, USA
3National Biological Service, Midwest Science Center, 4200 New Haven Road,
Columbia, Missouri 65201, USA

Received 3 April 1996; accepted in final form 28 August 1996

Abstract

  Understanding relationships between cationic metals such as cadmium, copper, nickel, lead and zinc, and amorphous iron sulfides, measured as acid volatile sulfide (AVS), is key to predicting metal bioavailability and toxicity in sediments. The objective of the present study was to assess seasonal and spatial variations of AVS in freshwater sediments contaminated with zinc. Sediments were sampled from three streams with varying levels of zinc contamination at two different times, March and June of 1995, representing cold- and warm-weather situations. Interstitial (pore) water concentrations of zinc, and solid phase concentrations of AVS and zinc were measured in surficial and deep sediment horizons. Toxicity tests (10-d) with the amphipod Hyalella azteca were conducted using intact cores. Sediment zinc concentrations from six sites within the primary test stream differed by about five-fold, and also varied seasonally. Acid volatile sulfide concentrations were generally lower than those of zinc, and pore water zinc concentrations typically were elevated. There was a positive correlation between solid-phase AVS and zinc concentrations, suggesting that the system was dominated by zinc, as opposed to iron sulfides. In contrast to expectations arising from some studies of seasonal variations of AVS in iron-dominated systems, AVS concentrations were smaller in June than in March. However, this was likely due to a major storm event and associated sediment scouring before the June sampling, rather than to seasonal processes related to variations in temperature and dissolved oxygen. Based upon an indirect analysis of depth variations in AVS, there was some indication that zinc sulfide might be less prone to oxidation than iron sulfide. There was a strong correlation between toxicity of the sediment samples to H. azteca and interstitial water concentrations of zinc; however, the possible contribution of other contaminants to sediment toxicity cannot be dismissed.

Keywords: sediment, acid volatile sulfide, zinc, interstitial water, bioavailability, toxicity

Journal of Aquatic Ecosystem Health: 5 (4); 255-264
 

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