| Row | Drug | Metabolites | Fish species | Dep-time | t1/2-hr | est | Sample | Ave Weight (gm) | Ave Water temp (°C) | Water | Dosage | Route | Comments | Protein binding | Cl | Vc | Vd | Authors | Date | Citation | Title | Genus Species | Drug Class | t1/2-detail | Wt gm-detail | Water temp (°C)-detail | Dosage-detail | Method | Authors-red | Row |
| 1 | Paraoxon | Rainbow trout | blood, plasma | 120 | 12 | Freshwater | 75 ng/ml 5 d | BATH | t1/2 > 24 hrs in cannulated fish. Within first 25 hrs about 1/4 dose is eliminated. Peak at less than 4 hr (113 ug). Residues peaked by 24 hrs with a plateau at approx 100 ng/ml remaining constant during the rest of the 140 hr exposure. | 28.1 L/kg/h | Abbas R, Hayton WL | 1997 | Toxicology and Applied Pharmacology 145:192-201 | A physiologically based pharmacokinetic and pharmacodynamic model for paraoxon in rainbow trout. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | >25 h | 100-140 g | 12 C | 75 ng/ml for 5 d | Absorbance | Abbas R, Hayton WL | 1 | |||||||
| 2 | Paraoxon | Rainbow trout | brain | 120 | 12 | Freshwater | 75 ng/ml 5 d | BATH | Residues peaked by 24 hrs with a plateau at approx 400 ng/m remaining constant during the rest of the 140 hr exposure. | Abbas R, Hayton WL | 1997 | Toxicology and Applied Pharmacology 145:192-201 | A physiologically based pharmacokinetic and pharmacodynamic model for paraoxon in rainbow trout. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | >25 h | 100-140 g | 12 C | 75 ng/ml for 5 d | Absorbance | Abbas R, Hayton WL | 2 | ||||||||
| 3 | Paraoxon | Rainbow trout | heart | 120 | 12 | Freshwater | 75 ng/ml 5 d | BATH | Residues peaked by 24 hrs with a plateau at approx 400 ng/m remaining constant during the rest of the 140 hr exposure. | Abbas R, Hayton WL | 1997 | Toxicology and Applied Pharmacology 145:192-201 | A physiologically based pharmacokinetic and pharmacodynamic model for paraoxon in rainbow trout. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | >25 h | 100-140 g | 12 C | 75 ng/ml for 5 d | Absorbance | Abbas R, Hayton WL | 3 | ||||||||
| 4 | Paraoxon | Rainbow trout | kidney | 120 | 12 | Freshwater | 75 ng/ml 5 d | BATH | Residues peaked by 24 hrs with a plateau at approx 80 ng/m remaining constant during the rest of the 140 hr exposure. | Abbas R, Hayton WL | 1997 | Toxicology and Applied Pharmacology 145:192-201 | A physiologically based pharmacokinetic and pharmacodynamic model for paraoxon in rainbow trout. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | >25 h | 100-140 g | 12 C | 75 ng/ml for 5 d | Absorbance | Abbas R, Hayton WL | 4 | ||||||||
| 5 | Paraoxon | Rainbow trout | liver | 120 | 12 | Freshwater | 75 ng/ml 5 d | BATH | Residues peaked by 24 hrs with a plateau at approx 900 ng/m remaining constant during the rest of the 140 hr exposure. | Abbas R, Hayton WL | 1997 | Toxicology and Applied Pharmacology 145:192-201 | A physiologically based pharmacokinetic and pharmacodynamic model for paraoxon in rainbow trout. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | >25 h | 100-140 g | 12 C | 75 ng/ml for 5 d | Absorbance | Abbas R, Hayton WL | 5 | ||||||||
| 6 | Paraoxon | Rainbow trout | 1 | blood, plasma | 345 | 12 | Freshwater | 75 ng/ml up to 120 hrs | BATH | Concentrations ng/ml during exposure- 0.25h=70.3, 0.5h=85.6, 1h=88.7, 1.5h=92.4, 2h=101.7, 4h=104.3, 6h=103.8, 12h=102.6, 24h=101.1, 48h=99.2, 72h=98.9 (rapid uptake and then plateau). | 2.78 L/kg/h | 1.04 L/kg | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 1996 | Toxicology and Applied Pharmacology 136:194-199 | Toxicokinetics of parathion and paraoxon in rainbow trout after intravascular administration and water exposure. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | 0.535 h | 140-550 g | 12 C | 75 ng/ml up to 120 hrs | GC | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 6 | |||||
| 7 | Paraoxon | Rainbow trout | 1 | blood, plasma | 440 | 12 | Freshwater | 5.7 mg/kg sd | IVC | Catheterized fish. Vd for paraoxon is 1080 mg/kg | 48% | 3.02 L/kg/h | 1.080 L/kg | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 1996 | Toxicology and Applied Pharmacology 136:194-199 | Toxicokinetics of parathion and paraoxon in rainbow trout after intravascular administration and water exposure. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | 0.528 h | 1330-550 g | 12 C | 5.7 mg/kg sd | GC | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 7 | ||||
| 8 | Parathion | Paraoxon | Rainbow trout | 56 | blood, plasma | 440 | 12 | Freshwater | 10 mg/kg sd | IVC | Paraoxon is a metabolite of parathion; Vd for parathion = 1370 ml/kg. Catheterized fish. | 98% | 0.021 L/kg/h | 1.370 L/kg | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 1996 | Toxicology and Applied Pharmacology 136:194-199 | Toxicokinetics of parathion and paraoxon in rainbow trout after intravascular administration and water exposure. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | 56.1 h | 1330-550 g | 12 C | 10 mg/kg sd | GC | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 8 | |||
| 9 | Parathion | Paraoxon | Rainbow trout | 57 | blood, plasma | 345 | 12 | Freshwater | 75 ng/ml up to 120 hrs | BATH | Paraoxon is a metabolite of parathion; Parathion concentration reached approx1.0 ug/ml in first 24 hr then declined to 0.4 slowly over the next 100 hr. | 0.183 L/kg/h | 1.280 L/kg | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 1996 | Toxicology and Applied Pharmacology 136:194-199 | Toxicokinetics of parathion and paraoxon in rainbow trout after intravascular administration and water exposure. | Oncorhynchus mykiss | Organic-Phosphorus-Pesticide | 57.3 h | 140-550 g | 12 C | 75 ng/ml up to 120 hrs | GC | Abbas R, Schultz IR, Doddapaneni S, Hayton WL | 9 | ||||
| 10 | Oxytetracycline | Chinook salmon | 88 | blood | 350 | 11 | Saltwater | 50 mg/kg sd | IVC | Lower Vd than expected in both spp, maybe because implanted cannula; bioavailability of OTC after PO are 24.84% (salmon) and 30.30% (trout) which are higher than normal; Vd= 0.89 l/kg - Chinook in seawater. OTC conc in blood went from 1000 ug/ml to approx 8 ug/ml in first 200 h, down to 1 by 900 h. AUC= 7126.8 ug h/ml | 0.89 L/kg | Abedini S, Namdari R, Law FCP | 1998 | Aquaculture 162:23-32 | Comparative pharmacokinetics and bioavailability of oxytetracycline in rainbow trout and Chinook salmon. | Oncorhynchus tshawytscha | Antibiotic-Tetracycline | 88.29 h | 350 g | 11 C | 50 mg/kg sd | HPLC | Abedini S, Namdari R, Law FCP | 10 | ||||||
| 11 | Oxytetracycline | Chinook salmon | 428 | blood | 350 | 11 | Saltwater | 50 mg/kg sd | PO | Chinook in seawater. Conc in bloold went from about 8 ug/ml to 2.5 in first 200 h and down to 1 by 900 h. | Abedini S, Namdari R, Law FCP | 1998 | Aquaculture 162:23-32 | Comparative pharmacokinetics and bioavailability of oxytetracycline in rainbow trout and Chinook salmon. | Oncorhynchus tshawytscha | Antibiotic-Tetracycline | 428.19 h | 350 g | 11 C | 50 mg/kg sd | HPLC | Abedini S, Namdari R, Law FCP | 11 | |||||||
| 12 | Oxytetracycline | Rainbow trout | 94 | blood | 350 | 11 | Freshwater | 50 mg/kg sd | IVC | Lower Vd than expected in both spp, maybe because implanted cannula; bioavailability of OTC after PO are 24.84% (salmon) and 30.30% (trout) which are higher than normal; Vd= 0.87l/kg. Conc went from 1000 ug/ml to approx 6 in first 200 h, then to 1 by 900h. AUC = 7781.2 ug h/ml. | 0.87 L/kg | Abedini S, Namdari R, Law FCP | 1998 | Aquaculture 162:23-32 | Comparative pharmacokinetics and bioavailability of oxytetracycline in rainbow trout and Chinook salmon. | Oncorhynchus mykiss | Antibiotic-Tetracycline | 94.22 h | 350 g | 11 C | 50 mg/kg sd | HPLC | Abedini S, Namdari R, Law FCP | 12 | ||||||
| 13 | Oxytetracycline | Rainbow trout | 479 | blood | 350 | 11 | Freshwater | 50 mg/kg sd | PO | Conc went from approx 8 ug/ml to 4 in first 200 h then to 1 by 900 h. | Abedini S, Namdari R, Law FCP | 1998 | Aquaculture 162:23-32 | Comparative pharmacokinetics and bioavailability of oxytetracycline in rainbow trout and Chinook salmon. | Oncorhynchus mykiss | Antibiotic-Tetracycline | 479.43 h | 350 g | 11 C | 50 mg/kg sd | HPLC | Abedini S, Namdari R, Law FCP | 13 | |||||||
| 14 | Sulfachlorpyridazine | Channel catfish | 4 | est | blood, plasma | 312 | 22 | Freshwater | 60 mg/kg sd | PO | t 1/2 est from graph. C-max 8.7 by 237 min. | Alavi FK, Rolf LL, Clarke CR | 1993 | J. Veterinary Pharmacology and Therapeutics 16:232-236 | The pharmacokinetics of sulfachlorpyridazine in channel catfish, Ictalurus punctatus. | Ictalurus punctatus | Antibiotic-Sulfa | 230 min (est from graph) | 312+/-220g | 22+/-2C | 60 mg/kg sd | Absorbance-Bratton&Marshall | Alavi FK, Rolf LL, Clarke CR | 14 | ||||||
| 15 | Sulfachlorpyridazine | Channel catfish | 5 | blood, plasma | 312 | 22 | Freshwater | 60 mg/kg sd | IC | conc went from approx 1100 ug/ml to 80 in first 200 min and down to 20 by 1h. | 4.63-14.20% | 0.077 L/kg/h | 0.043 L/kg | Alavi FK, Rolf LL, Clarke CR | 1993 | J. Veterinary Pharmacology and Therapeutics 16:232-236 | The pharmacokinetics of sulfachlorpyridazine in channel catfish, Ictalurus punctatus. | Ictalurus punctatus | Antibiotic-Sulfa | 230+/-65 min | 312+/-220g | 22+/-2C | 60 mg/kg sd | Absorbance-Bratton&Marshall | Alavi FK, Rolf LL, Clarke CR | 15 | ||||
| 16 | Malachite green | Leukomalachite green | Rainbow trout | gill | 70 | 18 | Freshwater | 1 mg/l 60 min | BATH | Residues decreased fairly rapidly during first 320 days reaching 260 by d41, and below 1 ng/g after 7th month. T 1/2 in the 20 d range initially, with later slow decline in the 50d range. | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 1997 | Rivista Italiana di Acquacoltura 32:45-60 | The persistence of malachite green in the edible tissue of rainbow trout (Oncorhynchus mykiss). | Oncorhynchus mykiss | Organic-Dye | 60-80 g | 18 C | 1 mg L 1 h | HPLC | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 16 | ||||||||
| 17 | Malachite green | Leukomalachite green | Rainbow trout | kidney | 70 | 18 | Freshwater | 1 mg/l 60 min | BATH | Max residue on d 30=1650 ng/g, declined to below 1 ng/g after 41 d. | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 1997 | Rivista Italiana di Acquacoltura 32:45-60 | The persistence of malachite green in the edible tissue of rainbow trout (Oncorhynchus mykiss). | Oncorhynchus mykiss | Organic-Dye | 60-80 g | 18 C | 1 mg L 1 h | HPLC | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 17 | ||||||||
| 18 | Malachite green | Leukomalachite green | Rainbow trout | muscle | 70 | 18 | Freshwater | 1 mg/l 60 min | BATH | Residues high for 34 days - above 1,000 ng/g. Decreased to 200 ng at the 4th month, around 100 by 150d, slowly declining to below 10 ng/g by 9th month. T 1/2 in the 40-50 d range. | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 1997 | Rivista Italiana di Acquacoltura 32:45-60 | The persistence of malachite green in the edible tissue of rainbow trout (Oncorhynchus mykiss). | Oncorhynchus mykiss | Organic-Dye | 60-80 g | 18 C | 1 mg L 1 h | HPLC | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 18 | ||||||||
| 19 | Malachite green | Leukomalachite green | Rainbow trout | skin | 70 | 18 | Freshwater | 1 mg/l 60 min | BATH | Residues decreased fairly rapidly during first 20 days, to about 2500 ng/g, d50=approx 1000, 200 ng/g round the 4th month, below 1 ng/g at day 283. t 1/2 in the 50d range. | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 1997 | Rivista Italiana di Acquacoltura 32:45-60 | The persistence of malachite green in the edible tissue of rainbow trout (Oncorhynchus mykiss). | Oncorhynchus mykiss | Organic-Dye | 60-80 g | 18 C | 1 mg L 1 h | HPLC | Alborali L, Sangiorgi E, Leali M, Guadagnini PF, Sicura S | 19 | ||||||||
| 20 | Malachite green | Rainbow trout | 15 | blood, serum | 199 | 8 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 2.15 h. C max 13 mg/ml 0h. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 15 h | 199 +/- 20 g | 7.7 +/-0.4 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 20 | |||||||
| 21 | Malachite green | Rainbow trout | 348 | blood, serum | 241 | 16 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 7.33 h C max 13.5 mg/ml 0h. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 348 h | 241 +/- 33g | 15.8 +/-0.8 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 21 | |||||||
| 22 | Malachite green | Rainbow trout | 139 | kidney | 241 | 16 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 6.46 h. C max348 ppm 0h. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 139 h | 241 +/- 33g | 15.8 +/-0.8 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 22 | |||||||
| 23 | Malachite green | Rainbow trout | 720 | kidney | 199 | 8 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 11.78 h. C mx 8 ppm 0h. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 720 h | 199 +/- 20 g | 7.7 +/-0.4 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 23 | |||||||
| 24 | Malachite green | Rainbow trout | 136 | liver | 241 | 16 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 1.98 h. C max 16.5 ppm 0h. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 136 h | 241 +/- 33g | 15.8 +/-0.8 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 24 | |||||||
| 25 | Malachite green | Rainbow trout | 331 | liver | 199 | 8 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 2.10 h C max 9 ppm 0h. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 331 h | 199 +/- 20 g | 7.7 +/-0.4 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 25 | |||||||
| 26 | Malachite green | Rainbow trout | 70 | muscle | 241 | 16 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 8.35 h. Cmax 10.8 ppm at 90-120 min | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 69.36 h | 241 +/- 33g | 15.8 +/-0.8 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 26 | |||||||
| 27 | Malachite green | Rainbow trout | 93 | muscle | 199 | 8 | Freshwater | 1.6 mg/L 40 min | BATH | t 1/2 alpha = 5.43 h Cmax 7.8 ppm at 90-120 min. | Alderman DJ, Clifton-Hadley RS | 1993 | J. Fish Diseases 16:297-311 | Malachite green: a pharmacokinetic study in rainbow trout, Oncorhynchus mykiss (Walbaum). | Oncorhynchus mykiss | Organic-Dye | 92.64 h | 199 +/- 20 g | 7.7 +/-0.4 C | 1.6 mg/L 40 min | Absorbance | Alderman DJ, Clifton-Hadley RS | 27 | |||||||
| 28 | Malachite green | Atlantic salmon | eggs | Not specified | 1 mg/l 1 h * | BATH | Residues in eggs taken from treated adults ranged d1=4.16-3.15, d2-d7= 0.72-3.6, d24-d41 = 0.21-2.29 ug/g. | Allen JL | 1990 | Investigations in Fish Control U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. 101:1-4 | Residues of Malachite Green in muscle, eggs, and fry of treated Atlantic salmon and Chinook salmon. | Salmo salar | Organic-Dye | Not specifed | Not specified | 1 ppm for 1 h for 20-47 treatments | Absorbance | Allen JL | 28 | |||||||||||
| 29 | Malachite green | Atlantic salmon | muscle | Not specified | 1 mg/l 1 h * | BATH | Residues highest (about 1.0 to 2.5 ug/g) in fish sampled 1 or 2 d after last treatment. At 5-7 d after treatment residues =0.64-2.22 ug/g. Residues after 24-41 d = 0.91-0.33 ug/g. | Allen JL | 1990 | Investigations in Fish Control U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. 101:1-4 | Residues of Malachite Green in muscle, eggs, and fry of treated Atlantic salmon and Chinook salmon. | Salmo salar | Organic-Dye | Not specifed | Not specified | 1 ppm for 1 h for 20-47 treatments | Absorbance | Allen JL | 29 | |||||||||||
| 30 | Malachite green | Chinook salmon | eggs | Not specified | 1 mg/l 1 h * | BATH | Residues in eggs taken from treated adults. Mean residues post treatment d1= 0.8-1.8, d6=0.97-1.86, d12-d18= 1.16-1.69 ug/g after 27-30 treatments. | Allen JL | 1990 | Investigations in Fish Control U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. 101:1-4 | Residues of Malachite Green in muscle, eggs, and fry of treated Atlantic salmon and Chinook salmon. | Oncorhynchus tshawytscha | Organic-Dye | Not specifed | Not specified | 1 ppm for 1 h for 27-30 treatments | Absorbance | Allen JL | 30 | |||||||||||
| 31 | Malachite green | Chinook salmon | muscle | Not specified | 1 mg/l 1 h * | BATH | Mean residues post treatment d1= 1.4, d6=0.61, d12-d18= 0.66 ug/g after 27-30 treatments. | Allen JL | 1990 | Investigations in Fish Control U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. 101:1-4 | Residues of Malachite Green in muscle, eggs, and fry of treated Atlantic salmon and Chinook salmon. | Oncorhynchus tshawytscha | Organic-Dye | Not specifed | Not specified | 1 ppm for 1 h for 27-30 treatments | Absorbance | Allen JL | 31 | |||||||||||
| 32 | Malachite green | Chinook salmon | whole body | Not specified | 1 mg/l 1 h * | BATH | Residues in newly hatched fry d1=0.9-1.04, d6=1.0-1.16, 12d-18d = 1.01-1.03 ug/g after 27-30 treatments. | Allen JL | 1990 | Investigations in Fish Control U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. 101:1-4 | Residues of Malachite Green in muscle, eggs, and fry of treated Atlantic salmon and Chinook salmon. | Oncorhynchus tshawytscha | Organic-Dye | Not specifed | Not specified | 1 ppm for 1 h for 27-30 treatments | Absorbance | Allen JL | 32 | |||||||||||
| 33 | Malachite green | Leuco MG | Rainbow trout | muscle+skin | 12 | Freshwater | 1 mg/L 1h sd | BATH | {14C]Malachite Green. Mean total residue d0= 1 ug/g, 5days withdrawal=0.4 ug/g. mean Leuko residue d0=47 ug/g, d5 withdrawal = 39 ug/g. the leuko metabolite was about 70-80% of the total residue. | Allen JL, Gofus JE, Meinertz JR | 1994 | J. AOAC International 77:553-557 | Determination of malachite green residues in the eggs, fry, and adult muscle tissue of rainbow trout (Oncorhynchus mykis). | Oncorhynchus mykiss | Organic-Dye | adult | 12 | 1 mg/L 1h sd | Rad | Allen JL, Gofus JE, Meinertz JR | 33 | |||||||||
| 34 | Malachite green | Rainbow trout | 48 | est | muscle | 14 | Freshwater | 0.1 mg/l 24 hr sd | BATH | Residues at 0 d = 1.87, 1 d = 1.17, 2 d = 0.72, 5 d = 0.28, 6 d = 0.22 ug/g after exposure for 24 hr. | Allen JL, Hunn JB | 1986 | Veterinary and Human Toxicology 28 (supp 1):21-24 | Fate and distribution studies of some drugs used in aquaculture. | Oncorhynchus mykiss | Organic-Dye | 48 h est | Not Specified | 14 | 0.1 mg/l for 24 hr sd | Absorbance | Allen JL, Hunn JB | 34 | |||||||
| 35 | MS-222 | meta-aminobenzoate ester | Channel catfish | blood | Freshwater | 100 mg/l | BATH | Tricaine methane sulphonate. After 0.5, 1.0, and 1.5 hour Withdrawal times in freshwater, residues of ms-222 were present in blood and brain. Liver and kidney samples could not be analyzed because the clean-up method used in this study was ineffective for these tissues | Allen JL, Luhning CW, Harmen PD (1970) | 1970 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.42 | Identification of MS-222 residues in selected fish tissues by thin layer chromatography. | Ictalurus punctatus | Anesthetic-Tricaine | Not Specified | Not Specified | 100ppm | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1970) | 35 | ||||||||||
| 36 | MS-222 | meta-aminobenzoate ester | Channel catfish | brain | Freshwater | 100 mg/l | BATH | Tricaine methane sulphonate. After 0.5, 1.0, and 1.5 hour Withdrawal times in freshwater, residues of ms-222 were present in blood and brain. Liver and kidney samples could not be analyzed because the clean-up method used in this study was ineffective for these tissues | Allen JL, Luhning CW, Harmen PD (1970) | 1970 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.42 | Identification of MS-222 residues in selected fish tissues by thin layer chromatography. | Ictalurus punctatus | Anesthetic-Tricaine | Not Specified | Not Specified | 100ppm | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1970) | 36 | ||||||||||
| 37 | MS-222 | meta-aminobenzoate ester | Channel catfish | muscle | Freshwater | 100 mg/l | BATH | Tricaine methane sulphonate. In muscle spiked with 0.2-10.0 ppm of ms-222 recoveries ranged from 25-60% | Allen JL, Luhning CW, Harmen PD (1970) | 1970 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.42 | Identification of MS-222 residues in selected fish tissues by thin layer chromatography. | Ictalurus punctatus | Anesthetic-Tricaine | Not Specified | Not Specified | 100ppm | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1970) | 37 | ||||||||||
| 38 | MS-222 | Acetylated metabolite | Muskellung | nearly 24 h | 24 | est | muscle | 1286 | 10 | Freshwater | 150 mg/l till deeply anesthetized | BATH | Tricaine methane sulphonate. Compared HPLC and TLC methods. Total MS222 free and acetylated residues ( ppm) at 0 h = 10.7, 2 h = 2.2, 24 h =2.0. (control had 1.2). | Allen JL, Luhning CW, Harmen PD (1972) | 1972 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.45 | Residues of MS-222 in Northern Pike, Muskellunge, and Walleye. | Esox masquinongy | Anesthetic-Tricaine | 24 | 544-770 gm | 10 C | 150 ppm till deeply anesthetized | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1972) | 38 | ||||
| 39 | MS-222 | Acetylated metabolite | Northern pike | nearly 24 h | 2 | est | muscle | 1286 | 17 | Freshwater | 150 mg/l till deeply anesthetized | BATH | Tricaine methane sulphonate. Compared HPLC and TLC methods. Total MS222 free and acetylated residues ( ppm) at 0 h =8.1 , 2 h = 0.5, 6 h = 0.5, 24 h =1.0. (control had 2.1). | Allen JL, Luhning CW, Harmen PD (1972) | 1972 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.45 | Residues of MS-222 in Northern Pike, Muskellunge, and Walleye. | Esox lucius | Anesthetic-Tricaine | 2 | 690-1180 gm | 17 C | 150 ppm till deeply anesthetized | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1972) | 39 | ||||
| 40 | MS-222 | Acetylated metabolite | Northern pike | nearly 24 h | 6 | est | muscle | 1286 | 12 | Freshwater | 150 mg/l till deeply anesthetized | BATH | Tricaine methane sulphonate. Compared HPLC and TLC methods. Total MS222 free and acetylated residues ( ppm) at 0 h =22.0 , 6 h = 0.7, 24 h =0.7. (control had 1.4).. | Allen JL, Luhning CW, Harmen PD (1972) | 1972 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.45 | Residues of MS-222 in Northern Pike, Muskellunge, and Walleye. | Esox lucius | Anesthetic-Tricaine | 6 | 690-1180 gm | 12 C | 150 ppm till deeply anesthetized | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1972) | 40 | ||||
| 41 | MS-222 | Acetylated metabolite | Northern pike | nearly 24 h | 6 | est | muscle | 1286 | 17 | Freshwater | 150 mg/l till deeply anesthetized | BATH | Tricaine methane sulphonate. Compared HPLC and TLC methods. Total MS222 free and acetylated residues ( ppm) at 0 h =12.2 , 6 h = 2.0, 24 h =1.1. (control had 1.8). | Allen JL, Luhning CW, Harmen PD (1972) | 1972 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.45 | Residues of MS-222 in Northern Pike, Muskellunge, and Walleye. | Esox lucius | Anesthetic-Tricaine | 6 | 690-1180 gm | 17 C | 150 ppm till deeply anesthetized | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1972) | 41 | ||||
| 42 | MS-222 | Acetylated metabolite | Northern pike | nearly 24 h | 24 | est | muscle | 1286 | 8 | Freshwater | 150 mg/l till deeply anesthetized | BATH | Tricaine methane sulphonate. Compared HPLC and TLC methods. Total MS222 free and acetylated residues ( ppm) at 0 h =11.3 , 2 h = 6.2, 24 h =1.3 (control had 2.0). | Allen JL, Luhning CW, Harmen PD (1972) | 1972 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.45 | Residues of MS-222 in Northern Pike, Muskellunge, and Walleye. | Esox lucius | Anesthetic-Tricaine | 24 | 690-1180 gm | 8 C | 150 ppm till deeply anesthetized | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1972) | 42 | ||||
| 43 | MS-222 | Acetylated metabolite | Northern pike | nearly 24 h | 24 | est | muscle | 1286 | 12 | Freshwater | 150 mg/l till deeply anesthetized | BATH | Tricaine methane sulphonate. Compared HPLC and TLC methods. Total MS222 free and acetylated residues ( ppm) at 0 h =9.1 , 2 h = 5.7, 24 h =2. (Control had 2.6). | Allen JL, Luhning CW, Harmen PD (1972) | 1972 | Investigations in Fish Control. U.S. Dept. of the Interior, Fish and Wildlife Service, Bureau of Sport Fisheries and Wildlife. SH157.7.I58 no.45 | Residues of MS-222 in Northern Pike, Muskellunge, and Walleye. | Esox lucius | Anesthetic-Tricaine | 24 | 690-1180 gm | 12 C | 150 ppm till deeply anesthetized | Absorbance-Bratton&Marshall, TLC | Allen JL, Luhning CW, Harmen PD (1972) | 43 | ||||
| 44 | MS-222 | Acetylated metabolite | Walleye |