title: Acute and chronic nitrite toxicity in juvenile pike-perch (Sander lucioperca) and its compensation by chloride.
abstract: Pike-perch Sander lucioperca is currently considered as one of the most promising candidates for production in freshwater recirculation aquaculture systems (RAS). Here, due to the lack of studies on nitrite (NO(2)(-)) toxicity in pike-perch, a flow-through exposure at 0, 0.44, 0.88, 1.75, 3.5, 7, 14 and 28 mg/L NO(2)(-)-N was carried out to determine the acute and chronic toxicity over a period of 32 days. In juvenile pike-perch, 120 h LC(50) was 6.1mg/L NO(2)(-)-N and at ≥14 mg/L NO(2)(-)-N all fish had died within 24 h. Chronic exposure revealed a significant build up of NO(2)(-) in the plasma as well as in the muscles at ≥0.44 mg/L NO(2)(-)-N peaking in fish exposed to the highest concentration of 3.5 mg/L NO(2)(-)-N after 32 days. Still, due to high individual variation methemoglobin (MetHb) was only significantly increased (p<0.01) at 3.5 mg/L NO(2)(-)-N. No adverse effects on red blood cells (RBC) and hematocrit were observed in any of the treatments. In a second experiment, compensation of NO(2)(-) toxicity at increasing chloride concentrations (40 (freshwater), 65, 90, 140, 240, 440 mg/L Cl(-)) was observed at a constant exposure of 10 mg/L NO(2)(-)-N for 42 days. At ≥240 mg/L Cl(-), NO(2)(-) build-up in blood plasma and muscle was completely inhibited. At lower Cl(-) concentrations (≤140 mg/L), NO(2)(-) was significantly increased in plasma, but only insignificantly elevated in muscle due to high individual variation. MetHb was increased significantly difference only at 40 mg/L Cl(-) (freshwater control) compared to the control. Again, high individual variations were observed. As a conclusion, S. lucioperca is moderately sensitive towards NO(2)(-) and acceptable levels in RAS should hence not exceed 1.75 mg/L NO(2)(-)-N to avoid MetHb formation. However, based on the 120 h LC(50) and a factor of 0.01 according to Sprague (1971), a NO(2)(-) concentration of ≤0.061 mg/L NO(2)(-)-N is considered as "safe." Thereby, no NO(2)(-) should accumulate in the plasma or muscle tissue during chronic exposure. For 10 mg/L NO(2)(-)-N, ≥240 mg/L chloride compensates for NO(2)(-) uptake in plasma and muscle.
authors: Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 310, 12587 Berlin, Germany. wuertz@igb-berlin.de
authors: S
authors: S
authors: Wuertz
authors: S G E
authors: SG
authors: Schulze
authors: U
authors: U
authors: Eberhardt
authors: C
authors: C
authors: Schulz
authors: J P
authors: JP
authors: Schroeder
mesh_terms: D000818:Animals; D049109:Cell Proliferation; D002712:Chlorides / Q000494:pharmacology*; D004781:Environmental Exposure / Q000032:analysis; D004847:Epithelial Cells / Q000187:drug effects / Q000473:pathology; D004906:Erythrocyte Count; D004912:Erythrocytes / Q000187:drug effects; D005880:Gills / Q000187:drug effects / Q000473:pathology; D007928:Lethal Dose 50; D008706:Methemoglobin / Q000378:metabolism; D009132:Muscles / Q000187:drug effects / Q000378:metabolism; D009573:Nitrites / Q000009:adverse effects* / Q000097:blood; D010471:Perches / Q000378:metabolism*; D016019:Survival Analysis; D023382:Toxicity Tests, Acute; D036401:Toxicity Tests, Chronic
chemical_list: D002712:Chlorides; D009573:Nitrites; D008706:Methemoglobin