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Ecotoxicological information

Short-term toxicity to fish

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Description of key information

The lowest LC50 for ammonia in fish is 0.083 mg/L ammonia (NH3).

Key value for chemical safety assessment

Fresh water fish

Fresh water fish
Dose descriptor:
Effect concentration:
0.083 mg/L

Additional information

A number of studies is available for aqueous ammonia and the read-across substances. In aqueous solution, ammonia exists primarily in two forms, un-ionized ammonia (NH3) and ammonium ion (NH4+), which are in equilibrium. As pH increases, the fraction of the total ammonia which is un-ionized increases. It is this un-ionized ammonia which is generally considered to be the primary cause of toxicity in aquatic systems. Ionised ammonia (NH4+) is of much lower toxicity than the non-ionised form (NH3). At environmentally relevant pHs, however, the substance will exist predominantly as the ionised form (NH4 +); the ammonium ion. The toxicity of ammonia is therefore dependent on pH, as pH will influence the proportion of total ammonia present as the non-ionised form. For clarity, the results are reported for the unionized form (NH3) if not stated otherwise.


The large dataset on the acute toxicity of ammonia to fish has recently (2007) been reviewed by the UK Environment Agency, in order to derive Environmental Quality Standards (EQSs) for this substance. The report states that the key study of acute fish toxicity is that of Rice & Bailey (1980) with ammonium sulphate, which identified a 96 -hour LC50 value in Oncorhyncus gorbuschka of 0.083 mg/L (NH3). Oncorhynchus gorbuscha (25 alvines /test vessel) were exposed to ammonium sulphate concentrations under static conditions in clean freshwater for 96 hours with no feeding. The acute LC50 value is reported to be 0.083 mg (NH3) under the conditions of this study (Rice & Bailey, 1980).


The toxicity of ammonia was investigated in the Fathead minnow (Pimephales promelas), using ammonium chloride (Thurston et al, 1983). The 96-h LC50 ranged from 0.75-3.4 mg/l unionized ammonia (34-109 mg/l total ammonia-N). The toxicity of ammonia decreased as temperature increased from 12-22⁰C. There was no significant relationship between ammonia toxicity and dissolved oxygen concentration, over the range of the latter from 3-9 mg/l. Toxicity was not related to the size or source of test fish.


The toxicity of ammonia to green sunfish (L. cyanellus) was studied by McCormick et al (1984). The 96 h LC50 concentrations at pH values of 6.6, 7.2, 7.7 and 8.7 were 0.5, 1.06, 1.34 and 1.73 mg NH3/L or 9, 57, 139 and 272 mg total ammonia /L, respectively.


The acute toxicity of ammonia to hatchery reared rainbow trout was measured in 86 flow-through tests, 96h -35 days long (Thurston et al, 1983). Fish ranged from 1 day old fry (<0.1 g) to 4 year old adults (2.6 kg). The 96h LC50 was 0.6-1.1 mg/l unionized ammonia (11-48 mg/l total ammonia N). Susceptibility to ammonia decreased as the fish developed from sac fry to juveniles and increased thereafter. Acute toxicity decreased as temperature increased from 12-19 °C. No significant differences in toxicity were observed in tests with different ammonium salts. The LC50 values obtained for 12 and 35 days were not different from those obtained earlier on in the test.


Thurston et al (1981) exposed S. gairdneri (rainbow trout) and S. clarki (cutthroat trout) to ammonium chloride for 96 hours. Concentration levels were either fixed or fluctuating. Fish were more tolerant of a fixed concentration than they were of fluctuating concentrations. The larger rainbow trout (> 2 kg) were more vulnerable to acutely toxic concentrations of ammonia than were smaller fish (20-300 g). The 96 hour LC50 for fixed ammonia concentrations in rainbow trout was 0.163 -0.500 mg unionised NH3/L. The 96 hour LC50 for fixed ammonia concentrations in cutthroat trout was 0.296 -0.327 mg unionised NH3/L.


The toxicity of ammonia was assessed in different developmental stages of rainbow trout (Salmo gairdneri (Oncorhynchus mykiss)) under flow-through conditions, with exposure to ammonium chloride (Calamari et al, 1981). The 96 - hour LC50 of ammonia in flow through conditions to rainbow trout at development stages from egg to hatch was > 0.486 mg unionised NH3/L, in fry stages was 0.160 - 0.370 mg unionised NH3/L, and in fingerling stages was 0.440 mg unionised NH3/L.


 The acute toxicity of ammonium chloride was investigated in Salmo namaycush and Salmo salar (Soderberg & Meade, 1992). The effects of calcium (present as CaCl2) and sodium (present as NaCl) on the toxicity of ammonia were also investigated in this study. Calcium did not reduce ammonia toxicity to Atlantic salmon fry or smelts. Sodium reduced toxicity to salmon smelts, but had no effect on toxicity to fry. Both sodium and calcium reduced toxicity to lake trout fingerlings, but had no effect on lake trout fry. Results suggest that mitigating effects of solution cations on un-ionized ammonia toxicity may be related to species, size, and life stage.


The influence of pH and temperature on the toxicity of ammonia was investigated by Dabrowski & Skiora (1986). Based on acute toxicity studies with common carp (Cyprinius carpio) the NH4Cl 48 hour LC50 mean range was 1.60-1.96 mg un-ionized NH3/L(equivalent to 103-109 mg total NH3/L). Ammonia toxicity increased with higher pH and lowered with increasing temperature.