Abstract

Water quality standards are essential for regulation of contaminants in marine environment. Seawater quality criteria (SWQC) for arsenic (As), cadmium (Cd) and lead (Pb) have not been developed for India. The aim of this study is to derive the SWQC for the metals based on Species Sensitivity Distribution (SSD). Eight species of sensitive marine organisms belonging to five phyla were assessed for their sensitivity to toxicity of As, Cd and Pb. Median effective concentrations (EC50) and Median Lethal Concentrations (LC50) were derived from the acute toxicity bio-assays. No Observed Effect Concentrations (NOEC), Lowest Observed Effect Concentrations (LOEC) and chronic values were derived from chronic toxicity bio-assays. Diatoms were more sensitive to As with 96 h EC50 of 0.1 mg/l and copepods were more sensitive to Cd and Pb with 96 h EC50 of 0.019 mg/l and 0.05 mg/l respectively. Estimated NOECs ranged from 4.87 to 21.55 µg/l of As, 1.0 to 120 µg/l of Cd and 5.67 to 91.67 µg/l of Pb. Similarly, chronic values (µg/l) were in the range of 6.71–26.1, 1.38–170, and 7.67–91.67 of As, Cd and Pb respectively. The Criterion Maximum Concentration (CMC), Criterion Continuous Concentration (CCC) and Predicted No Effect Concentration (PNEC) values were prescribed as SWQC. The CMC (µg/l) of 19, 1.7 and 17 for As, Cd, and Pb were derived respectively for acute exposure during accidental marine outfalls. The CCC (µg/l) for As was 4.6, 1.1 for Cd and 5.9 for Pb are recommended as SWQC for protection of 95% of marine organisms. PNEC (µg/l) of 3.8 for As, 0.92 for Cd and 4.3 for Pb are suggested for highly disturbed ecosystems, shell fishing and mariculture uses of water bodies. These values are recommended as a baseline for site specific water quality criteria for the coastal waters of the country.

Highlights

  • Coastal waters are under serious risk from pollutants due to the ever increasing anthropogenic activities viz., shipping, fishing, industrial settlements, tourism and urban development

  • The effective/lethal con­ centration (EC50/LC50) values were derived from Probit transformed regression lines of growth inhibition and mortality data of acute toxicity bio-assays

  • Whereas the No Observed Effect Concentrations (NOEC), Lowest Observed Effect Concentrations (LOEC) and chronic values were ob­ tained from the growth and mortality responses of all the organisms during sub-lethal exposure bio-assays based on statistical multiple comparison with control (i.e. Dunnett’s t-test; p ≤ 0.05)

Read more

Summary

Introduction

Coastal waters are under serious risk from pollutants due to the ever increasing anthropogenic activities viz., shipping, fishing, industrial settlements, tourism and urban development. The water quality standards are developed using the toxicity data on the sensitive organisms (Stephen et al, 1985). Environmental agencies are updating the toxicity data in databases that are useful in upgrading/deriving water quality standards. The parameters like sensitivity of the species, life stage, duration of the experiment, chemical purity, speciation, measured concentration of toxicants, toxicity endpoints, toxicity response and water quality parameters are documented for updating databases. Such databases are opening the opportunities to develop, update and strengthen the regulatory standards and risk assessment. SSD helps in identifying the environ­ mental risk using the toxicity data from the stressor that will affect the proportion of species at particular concentration

Objectives
Methods
Results
Discussion
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