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Short-Term Guideline Values for Chlorine in Freshwaters.
Graeme E Batley1, Merrin S Adams1, Stuart L Simpson1
1Centre for Environmental Contaminants Research, CSIRO Land and Water, Kirrawee, New South Wales, Australia.
Environmental Toxicology and Chemistry
|January 19, 2021
Summary
New Australian freshwater guidelines for total residual chlorine (TRC) are proposed. Based on rapid chlorine decomposition and acute toxicity, revised values of 7 µg Cl/L for hypochlorite and 9 µg Cl/L for chloramine are suggested for 95% species protection.
Area of Science:
- Environmental toxicology
- Aquatic toxicology
- Water quality guidelines
Background:
- Current Australian and New Zealand freshwater guideline value for total residual chlorine (TRC) is 3 µg Cl/L.
- This value is based on acute toxicity data converted to chronic data using a default ratio, without accounting for chlorine's rapid decomposition.
- Chlorine in freshwater rapidly decomposes from hypochlorite to chloramine.
Purpose of the Study:
- To review the literature on chlorine's fate and ecotoxicity in freshwater.
- To derive revised default guideline values for hypochlorite and chloramine in freshwater.
- To recommend guideline values based on acute toxicity due to rapid chlorine decomposition.
Main Methods:
- Literature review on chlorine fate and ecotoxicity in freshwater.
- Application of species sensitivity distribution (SSD) to toxicity data.
- Derivation of guideline values for 95% species protection.
Main Results:
- Revised guideline values for 95% species protection were derived: 7 µg Cl/L for hypochlorite and 9 µg Cl/L for chloramine.
- The hypochlorite value is applicable to any TRC-containing effluent.
- The chloramine value is more appropriate for drinking water effluents where dechlorination has occurred.
Conclusions:
- Revised guideline values for TRC in freshwater are proposed, considering chlorine's decomposition.
- The proposed values are 7 µg Cl/L (hypochlorite) and 9 µg Cl/L (chloramine) for 95% species protection.
- These values are likely conservative and should be applied at the edge of the mixing zone, potentially using time-weighted averages.
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