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. 2017 Mar 30;5(1):31–33. doi: 10.14252/foodsafetyfscj.2016031s

Isofetamid (Pesticides)

Food Safety Commission of Japan
PMCID: PMC6989172  PMID: 32231927

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


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