Abstract
The Food Safety Commission of Japan (FSCJ) conducted a risk assessment of isofetamid (CAS No. 875915-78-9), a phenacyl amide fungicide, based on results from various studies. Major treatment-related effects of isofetamid were observed on liver (hepatocellular hypertrophy) and on thyroid (hypertrophy of follicular epithelial cell). None of neurotoxicity, carcinogenicity, reproductive toxicity, teratogenicity, immunotoxicity and genotoxicity were observed. Based on the results from various studies, only parent isofetamid was identified as the relevant substance to the residue definition for dietary risk assessment in agricultural products. The lowest no-observed-adverse-effect level (NOAEL) obtained in all the toxicity studies was 5.34 mg/kg bw/day in a one-year chronic toxicity study in dogs. FSCJ has established an acceptable daily intake (ADI) of 0.053 mg/kg bw/day, applying a safety factor of 100 to the NOAEL. The lowest NOAEL for adverse effects that would be likely to be elicited by a single oral administration of isofetamid was 300 mg/kg bw/day, which is obtained on the maternal toxicity in rabbits. FSCJ specified an acute reference dose (ARfD) of 3 mg/kg bw/day, applying a safety factor of 100 to the NOAEL.
Conclusion in Brief
The Food Safety Commission of Japan (FSCJ) conducted a risk assessment of isofetamid (CAS No. 875915-78-9), a phenacyl amide fungicide, based on results from various studies.
The data used in the assessment include the fate in animals (rats, goats and chickens), fate in plants (lettuce and grapes), residues in crops, subacute toxicity (rats, mice and dogs), subacute neurotoxicity (rats), chronic toxicity (rats and dogs), carcinogenicity (rats and mice), two-generation reproductive toxicity (rats), developmental toxicity (rats and rabbits), immunotoxicity (mice), genotoxicity, and also a study on the toxic mechanisms.
Major treatment-related effects of isofetamid were observed on liver (hepatocellular hypertrophy) and on thyroid (hypertrophy of follicular epithelial cell). None of neurotoxicity, carcinogenicity, reproductive toxicity, teratogenicity, immunotoxicity and genotoxicity were observed.
Based on the results from various studies, only parent isofetamid was identified as the relevant substance to the residue definition for dietary risk assessment in agricultural products.
The lowest no-observed-adverse-effect level (NOAEL) obtained in all the toxicity studies was 5.34 mg/kg bw/day in a one-year chronic toxicity study in dogs. FSCJ has established an acceptable daily intake (ADI) of 0.053 mg/kg bw/day, applying a safety factor of 100 to the NOAEL.
The lowest NOAEL for adverse effects that would be likely to be elicited by a single oral administration of isofetamid was 300 mg/kg bw/day, which is obtained on the maternal toxicity in rabbits. FSCJ specified an acute reference dose (ARfD) of 3 mg/kg bw/day, applying a safety factor of 100 to the NOAEL.(table 1, 2)
Table 1. Levels relevant to toxicological evaluation of isofetamid.
| Species | Study | Dose (mg/kg bw/day) |
NOAEL (mg/kg bw/day) |
LOAEL (mg/kg bw/day) |
Critical endpoints1) |
|---|---|---|---|---|---|
| Rat | 90-day subacute toxicity study |
0, 100, 1,000, 10,000 ppm M: 0, 6.65, 68.9, 637 F: 0, 7.83, 78.0, 741 |
M: 6.65 F: 7.83 |
M: 68.9 F: 78.0 |
F/M: Diffuse Hepatocellular hypertrophy, etc |
| 90-day subacute neurotoxicity study |
0, 500, 3,000, 15,000 ppm M: 0, 34, 207, 1,050 F: 0, 40, 245, 1,210 |
M: 207 F: 1,210 |
M: 1,050 F: - |
M: Depressed body weight F: No toxicological effects (Not neurotoxic) |
|
| One-year chronic toxicity study |
0, 30, 100, 500, 5,000 ppm M: 0, 1.39, 4.68, 22.7, 237 F: 0, 1.82, 5.92, 30.0, 311 |
M: 22.7 F: 30.0 |
M: 237 F: 311 |
F/M: Increased absolute/relative liver weights, Diffuse hepatocellular hypertrophy, etc |
|
| Two-year carcinogenicity study |
0, 30, 100, 500, 5,000 ppm M: 0, 1.21, 4.07, 20.3, 210 F: 0, 1.55, 5.02, 26.1, 263 |
M: 20.3 F: 26.1 |
M: 210 F: 263 |
F/M: Hypertrophy of thyroid follicular epithelial cell, etc (Not carcinogenic) |
|
| Two-generation reproductive toxicity study |
0, 100, 1,000, 10,000 ppm PM: 0, 5.76, 57.1, 594 PF: 0, 8.85, 90.5, 908 F1M: 0, 6.02, 60.1, 643 F1F: 0, 8.69, 89.1, 906 |
Parent PM: 57.1 PF: 8.85 F1M: 60.1 F1F: 8.69 |
Parent PM: 594 PF: 90.5 F1M: 643 F1F: 89.1 |
Parent F/M: Increased absolute/ relative liver weights, etc. |
|
| Offspring PM: 57.1 PF: 90.5 F1M: 60.1 F1F: 89.1 |
Offspring PM: 594 PF: 908 F1M: 643 F1F: 906 |
Offspring F/M: Depressed body weight, etc. (No effect on reproduction) |
|||
| Developmental toxicity study |
0, 100, 300, 1,000 | Maternal:
300 Embryo/fetus: 1,000 |
Maternal: 1,000 Embryo/fetus: - |
Maternal: Trend in increased absolute liver weights and increased relative liver weights Embryo/fetus: No toxicologi- cal effects (Not teratogenic) |
|
| Mouse | 90-day subacute toxicity study | 0, 100, 1,000, 8,000 ppm M: 0, 13, 129, 1,070 F: 0, 16, 161, 1,310 |
M: 129 F: 161 |
M: 1,070 F: 1,310 |
F/M: Increased absolute/ relative liver weights, etc |
| 78-week carcinogenicity study |
0, 100, 800, 3,000(F),
4,000(M) ppm M: 0, 12, 92, 502 F: 0, 14, 118, 431 |
M: 12 F: 118 |
M: 92 F: 431 |
F/M: Depressed body weight, etc (Not carcinogenic) |
|
| Rabbit | Developmental toxicity study |
0, 100, 300, 1,000 | Maternal: 300 Embryo/fetus: 1,000 |
Maternal: 1,000 Embryo/fetus: - |
Maternal: Depressed body weight, etc Embryo/fetus: No toxicologi- cal effects (Not teratogenic) |
| Dog | 90-day subacute toxicity study | 0, 100, 1,000, 10,000 ppm M: 0, 2.95, 29.3, 301 F: 0, 3.07, 32.7, 314 |
M: 2.95 F: 3.07 |
M: 29.3 F: 32.7 |
F/M: Increase in ALP, etc |
| One-year chronic toxicity study | 0, 60, 200, 6,000 ppm M: 0, 1.61, 5.34, 166 F: 0, 1.57, 5.58, 178 |
M: 5.34 F: 5.58 |
M: 166 F: 178 |
F/M: Increased absolute/ relative liver weight, Centrilobular hypertrophy of hepatocytes, etc |
|
| ADI | NOAEL: 5.34 SF: 100 ADI: 0.053 |
||||
| The critical study for setting ADI | One-year chronic toxicity study in dogs | ||||
M, Male; F, Female; F/M, both sexes; PM, Male in P (Parent) generation; PF, Female in P generation; F1M, Male in F1 generation; F1F, Female in F1 generation; -, LOAEL was not derived; 1), The adverse effect observed at LOAEL; ADI, Acceptable daily intake; SF, Safety factor
Table 2. Adverse effects possibly elicited by a single oral administration.
| Species | Study | Dose (mg/kg bw/day) | NOAEL and end point for establishing acute reference dose (ARfD)1) (mg/kg bw/day) |
|---|---|---|---|
| Rabbit | Developmental toxicity study | 0, 100, 300, 1,000 | Maternal: 300 Maternal: Depressed body weight gain, lower feed consumption (gestation day 6 to 9) |
| ARfD | NOAEL: 300 SF: 100 ARfD: 3 |
||
| The critical study for setting ARfD | Developmental toxicity study in rabbits | ||
1), The adverse effect observed at LOAEL; ARfD, Acute reference dose; SF, Safety factor
Acknowledgement:
FSCJ wishes to thank the members of Expert Committee on Pesticides for the preparation of the original full report.
This is an English translation of excerpts from the original full report (October 2016-FS/641/2016). Only original Japanese texts have legal effects. The original full report is available in Japanese at http://www.fsc.go.jp/fsciis/attachedFile/download?retrievalId=kya20150113247&fileId=201
