Abstract

The toxicity of common compounds of lead, cadmium and zinc was evaluated in waters similar to that found in the world’s largest lead producing area in Missouri. Static, acute toxicity tests were performed using fathead minnows (Pimephales promelas) and water fleas (Daphnia magna) respectively. Test organisms were subjected to varying amounts of sulfide, carbonate, chloride and sulfate salts of lead, zinc and cadmium mixed in hard, alkaline waters typical to this region. Median lethal concentrations were calculated using nominal versus measured metal concentrations. Measured metal concentrations included four different metal fractionation (extraction/filtration) techniques at different pH levels which included “dissolved”, “available”, “easily dissolved” and “total” metals. Most consistent correlations between mortality and metal concentrations were found with the “Total” or “Nominal” values. The “Easily Dissolved” metals which corresponded to acid soluble criteria did not effectively represent toxicity and bioavailability of metals. A metal speciation model, MINTEQA2, was used to predict the concentrations of the dissolved metal species at the pH levels commonly seen in the toxicity test vessels. MINTEQ model results suggested that analysis of metals in aqueous environment is better understood when examining speciation characteristics and would likewise be a better mechanism to develop site-specific water quality criteria for metals.

Highlights

  • The aquatic toxicity of metals is a complicated phenomena involving interactions between the environment and the metal pollutants of concern

  • Results of static acute toxicity tests using the sulfide, carbonate, chloride and sulfate salts of lead, cadmium and zinc performed on fathead minnows and daphnids are displayed in Tables 1, 2, and 3

  • Static acute toxicity tests using fathead minnows and daphnids showed that various lead, zinc, and cadmium salts were much less toxic in hard, alkaline waters that are typical of the New Lead Belt streams and rivers

Read more

Summary

Introduction

The aquatic toxicity of metals is a complicated phenomena involving interactions between the environment and the metal pollutants of concern. Predicting the toxic effect that metals have in natural waters requires evaluating the bioavailability of the metal pollutants. The term “bioavailability” reflects the premise that for some heavy metals organisms may be exposed to less than the total amount present in their habitat (Schmitt et al, 1987). The extent to which heavy metals react with and affect biological components is immensely influenced by the physicochemical factors of the specific environment. Many chemical characteristics of the water are important in defining both the chemical species of the metal present and physiological status of the organism being tested. Further investigations suggested that evaluation of the toxic bioavailability of metals is dependent on the chemical complexation and speciation (Black et al, 1973; Vuceta and Morgan, 1978; Stumm and Morgan, 1981; Davis et al, 1992, 1993)

Methods
Results
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call