T- toxicological evaluation
** Evaluated within the Periodic Review Programme of the Codex Committee on Pesticide Residues
TOXICOLOGY
Terbufos is an organophosphorus compound classified as a systemic insecticide and nematocide which was last evaluated by the JMPR in 1989 when an ADI of 0-0.0002 mg/kg bw was established. Terbufos was considered by the present Meeting within the periodic review programme of the Codex Committee on Pesticide Residues.
In rats, absorption of single doses of [14C]terbufos was rapid and fairly complete. Most of the radiolabel was excreted within 24-48 h. Excretion was primarily by the urinary route (about 70-80% of the administered dose). Terbufos was extensively metabolized and little radioactivity was found in the tissues. There were no significant sex-specific differences in the toxicokinetics of terbufos.
Sulfoxidation and desulfuration of terbufos is followed by hydrolysis of the thiolophosphorus bond (S-P), enzymatic S-methylation and then additional S-oxidation. On the basis of a 14-day study of repeated doses, terbufos showed little potential for bioaccumulation.
By analogy with other phosphorodithioate compounds, it is likely that terbufos is metabolically activated to terbufos oxon and other oxons, which cause inhibition of acetylcholinesterase activity.
Terbufos is of very high acute toxicity when administered by oral, dermal, and inhalation routes. Acute LD50 values in rodents and dogs were similar, ranging from 1.4 to 9.2 mg/kg bw when administered orally. Clinical signs observed were those typical of cholinergic toxicity.
The acute LD50 for terbufos administered dermally was about 1 mg/kg bw in rabbits. A single application of undiluted terbufos to the shaved skin (0.25-0.5 ml) or into the conjunctival sac (0.1 ml) of rabbits killed all animals within 24 h. The acute LC50 for terbufos administered by inhalation ranged from 0.0012 to 0.0061 mg/l in rats.
In studies in rats and dogs, the critical effects of repeated doses of terbufos were inhibition of brain cholinesterase activity and associated clinical signs. NOAELs for inhibition of brain cholinesterase activity in these studies ranged from about 0.04 to 0.11 mg/kg bw per day and LOAELs ranged from about 0.085 to 0.55 mg/kg bw per day. Inhibition of brain cholinesterase activity of 7-12%, in the absence of clinical signs, was not considered toxicologically relevant. NOAELs and LOAELs for inhibition of erythrocyte cholinesterasese activity were not substantially different from those for inhibition of brain cholinesterase activity.
In a 1-year study in dogs given terbufos in capsule form, the NOAEL was 0.060 mg/kg bw per day on the basis of inhibition of brain acetylcholinesterase activity at 0.090 mg/kg bw per day. The NOAELs for inhibition of brain acetylcholinesterase activity in other short-term studies in dogs were consistent with that of the 1-year study.
In an 18-month study in mice fed with terbufos, there was no evidence of carcinogenicity at doses considered relevant for risk assessment. Cholinesterase activities were not measured. The NOAEL was 3 ppm (equivalent to 0.45 mg/kg bw per day) on the basis of significant decreases in body weights at the next higher dose of 6 ppm (equivalent to 0.9 mg/kg bw per day).
A 2-year study of toxicity and carcinogenicity in rats had limitations which included outstanding questions involving the etiology and/or relationship to treatment of certain non-neoplastic findings, confounding by non-treatment related illness in test animals and the lack of supporting data to adequately quantify dietary intake, stability, and homogeneity. However, on the basis of inhibition of brain cholinesterase activity in animals receiving the highest dose, this study was considered to be adequate for testing for carcinogenicity. No increase in tumour incidence was observed after a histopathological re-evaluation of tissues for the assessment of carcinogenic potential. The NOAEL was 1 ppm (equivalent to 0.05 mg/kg bw per day) on the basis of inhibition of brain acetylcholinesterase activity at 4 ppm (equivalent to 0.2 mg/kg bw per day).
This conclusion was supported by a subsequently conducted 1-year study of toxicity in rats, in which no significant systemic or neoplastic effects were observed. The NOAEL was 1 ppm (equal to 0.055 mg/kg bw per day) on the basis of the absence of significant inhibition of brain acetylcholinesterase activity at all doses.
The Meeting concluded that terbufos was not carcinogenic in mice or rats.
The genotoxic potential of terbufos was assessed in an adequate range of in vitro and in vivo tests. Based on the overall weight of evidence from the studies of genotoxicity, the Meeting concluded that terbufos is unlikely to pose a genotoxic risk to humans.
In view of the lack of significant genotoxicity and the absence of carcinogenicity observed, the Meeting concluded that terbufos is unlikely to pose a carcinogenic risk to humans.
In a study of reproductive toxicity study in rats, mortality and clinical signs of toxicity in females, some occurrences of excess salivation in males and decreases in body weight and food consumption in both sexes were observed at 5 ppm (equal to 0.42 mg/kg bw per day), a treatment that was terminated prematurely. At a dose of 2.5 ppm, an increase in soft stools and body-weight loss was noted in lactating females. Also observed were decreases in pregnancy rate, male fertility and significant decreases in the mean body weight of viable pups on days 14 and 21 of lactation in P1 and F1 litters. The NOAEL for these effects on reproduction and offspring was 1.0 ppm (equal to 0.086 mg/kg bw per day). Inhibition of brain cholinesterase activity was observed in both sexes, with a NOAEL of 0.5 ppm (equal to 0.043 mg/kg bw per day).
In a study of developmental toxicity in rats, the NOAEL for maternal and developmental effects was 0.2 mg/kg bw per day, the highest dose tested. Mortality was seen at a dose of 0.4 mg/kg bw per day in a preliminary study.
In a study of developmental toxicity in rabbits, the NOAEL for maternal and developmental effects was 0.25 mg/kg bw per day on the basis of clinical and systemic findings in does, an increased number of does with resorption sites and decreased fetal body weights at the next highest dose of 0.50 mg/kg bw per day.
The potential of terbufos to induce delayed polyneuropathy in hens when given as a single dose by gavage was assessed. The activity of neuropathy target esterase was not measured in this study. No significant changes in spinal cord and peripheral nerves were apparent in the group treated with terbufos. The Meeting concluded that at doses relevant to dietary exposure in humans, there was no concern for the induction of delayed polyneuropathy by terbufos.
In a study of neurotoxicity in which terbufos was given as a single dose by gavage to rats, mortality, clinical signs of toxicity, including miosis, and inhibition of brain and erythrocyte cholinesterase activities were noted at the highest dose tested of 0.90 mg/kg bw. The only finding at the intermediate dose (0.30 mg/kg bw) was miosis, which was observed in the absence of inhibition of concurrently measured brain and erythrocyte cholinesterase activities. No neurohistopathological lesions were found at any dose. The NOAEL was 0.15 mg/kg bw on the basis of findings of miosis in both sexes at the next highest dose of 0.30 mg/kg bw.
A 13-week study of neurotoxicity was conducted in rats. Other than a slight decrease in body weight and inhibition of brain and erythrocyte cholinesterase activities at the high dose of 3.0 ppm (equal to 0.25 mg/kg bw per day), no effects (including miosis) were observed. The NOAEL was 0.8 ppm (equal to 0.059 mg/kg bw per day) on the basis of inhibition of brain acetylcholinesterase activity at 0.25 mg/kg bw per day.
The acute oral toxicity of a number of metabolites of terbufos was evaluated in female mice. LD50s were as follows: 1.1 mg/kg bw (terbufoxon sulfoxide), 3.4 mg/kg bw (terbufos sulfoxide), 3.4 mg/kg bw (terbufoxon sulfone), 14 mg/kg bw (terbufos sulfone), 2.2 mg/kg bw (terbufoxon), 3670 mg/kg bw (methane, bis (tert-butylsulfonyl) and > 2500 mg/kg bw (methane, (tert-butylsulfinyl)(methylsulfinyl)).
In a comparative 14-day study in dogs, terbufos given in capsules was found to be more toxic than either terbufos sulfoxide or terbufos sulfone.
There have been a number of reports of occupational and non-occupational poisoning incidents associated with exposure to terbufos. No information was available regarding possible effects from terbufos manufacturing facilities.
The Meeting concluded that the existing database on terbufos was adequate to characterize the potential for hazard to fetuses, infants and children.
Toxicological evaluation
The Meeting established an ADI of 0-0.0006 mg/kg bw based on an overall NOAEL of 0.06 mg/kg bw per day and a safety factor of 100 for inhibition of brain cholinesterase activity, in the 1-year toxicity study, the 13-week study of neurotoxicity and the two-generation study of reproduction in rats, and the 1-year study in dogs.
The Meeting established an acute RfD of 0.002 mg/kg bw based on a NOAEL of 0.15 mg/kg bw per day for miosis in the study of neurotoxicity in rats given a single dose of terbufos, and a 100-fold safety factor. Since only in this study miosis was observed in the absence of inhibition of cholinesterase activity, it may be possible to refine the acute RfD after better characterization of this effect.
Levels relevant to risk assessment
Species |
Study |
Effect |
NOAEL |
LOAEL |
Mouse |
18-month study of toxicity and carcinogenicitya |
Toxicity |
3 ppm, equivalent to 0.45 mg/kg bw per day |
6 ppm, equivalent to 0.90 mg/kg bw per day |
Carcinogenicity |
12 ppm, equivalent to 1.8 mg/kg bw per dayd |
- |
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Rat |
2-year study of toxicity and carcinogenicitya |
Carcinogenicity |
4 ppm, nominally equivalent to 0.2 mg/kg bw per dayd |
- |
1-year study of toxicitya |
Toxicity |
1 ppm, equal to 0.055 mg/kg bw per dayd |
- |
|
13-week study of neurotoxicitya |
Toxicity |
0.8 ppm, equal to 0.059 mg/kg bw per day |
3.0 ppm, equal to 0.25 mg/kg bw per day |
|
Single-dose study of neurotoxicityb |
Toxicity |
0.15 mg/kg bw per day |
0.30 mg/kg bw per day |
|
Multi-generation study of reproductive toxicitya |
Parental toxicity |
0.5 ppm, equal to 0.043 mg/kg bw per day |
1.0 ppm, equal to 0.086 mg/kg bw per day |
|
Offspring toxicity |
1.0 ppm, equal to 0.086 mg/kg bw per day |
2.5 ppm, equal to 0.21 mg/kg bw per day |
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Study of developmental toxicityb |
Maternal toxicity |
0.20 mg/kg bw per dayd |
- |
|
Embryo- and fetotoxicity |
0.20 mg/kg bw per dayd |
- |
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Rabbit |
Study of developmental toxicityb |
Maternal toxicity |
0.25 mg/kg bw per day |
0.50 mg/kg bw per day |
Embryo- and fetotoxicity |
0.25 mg/kg bw per day |
0.50 mg/kg bw per day |
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Dog |
1-year study of toxicityc |
Toxicity |
0.06 mg/kg bw per day |
0.09 mg/kg bw per day |
a Diet
b Gavage
c Capsule
d Highest dose tested
Estimate of acceptable daily intake for humans
0-0.0006 mg/kg bw
Estimate of acute reference dose
0.002 mg/kg bw
Studies that would provide information useful for the continued evaluation of the compound
- A study of delayed neurotoxicity with neuropathy target esterase measurements (known to be ongoing)
- Further observations in humans
- Characterization of miosis
Summary of critical end-points for terbufos
Absorption, distribution, excretion and metabolism in mammals |
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Rate and extent of oral absorption |
Rapid and fairly complete |
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Dermal absorption |
No specific study; rapidly penetrating following dermal or ocular application |
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Distribution |
Relatively rapid and fairly complete |
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Potential for accumulation |
Little |
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Rate and extent of excretion |
Relatively rapid and complete; most eliminated in 24 to 48 h; elimination in urine predominates |
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Metabolism in animals |
Sulfoxidation and desulfuration of terbufos is followed by hydrolysis of the thiolophosphorus bond (S-P), enzymatic S-methylation and then additional S-oxidation |
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Toxicologically significant compounds |
Terbufos |
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Acute toxicity |
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Rat, LD50, oral |
1.4-9.0 mg/kg bw |
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Rabbit, LD50, dermal |
0.81-0.93 mg/kg bw |
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Rat, LC50, inhalation |
Vapour, 4-h whole body exposure: 0.0012-0.0061 mg/l |
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Rabbit, skin irritation |
Could not be determined due to lethality |
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Rabbit, eye irritation |
Could not be determined due to lethality |
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Skin sensitization |
Not determined owing to potential for severe toxicity |
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Short-term studies of toxicity |
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Target/critical effect |
Inhibition of brain cholinesterase activity |
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Lowest relevant oral NOAEL |
0.059 mg/kg bw per day (13-week study of neurotoxicity in rats) |
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Lowest relevant dermal NOAEL |
Data not available |
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Lowest relevant inhalation NOAEL |
No appropriate data available |
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Genotoxicity |
Unlikely to be genotoxic |
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Long-term studies of toxicity and carcinogenicity |
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Target/critical effect |
Inhibition of brain cholinesterase activity |
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Lowest relevant NOAEL |
0.055 mg/kg bw per day (1-year study in rats) |
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Carcinogenicity |
No evidence of carcinogenicity; Unlikely to pose a risk to humans |
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Reproductive toxicity |
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Reproduction target/critical effect |
Decreases in male fertility and female pregnancy rate |
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Lowest relevant reproductive NOAEL |
0.086 mg/kg bw per day (rats) |
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Developmental target/critical effect |
Not teratogenic; Reduced fetal body weight |
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Lowest relevant developmental NOAEL |
0.25 mg/kg bw per day (rabbits) |
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Neurotoxicity/delayed neurotoxicity |
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Acute neurotoxicity |
|
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Target/critical effect |
Miosis |
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Relevant NOAEL |
0.15 mg/kg bw (rats) |
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13-week study of neurotoxicity |
|
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Target/critical Effect |
Inhibition of brain cholinesterase activity |
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Relevant NOAEL |
0.059 mg/kg bw per day (rats) |
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Delayed neuropathy |
No evidence to suggest toxicity at dietary exposures |
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Medical data |
There have been a number of reports of occupational and non-occupational poisoning incidents associated with exposure to terbufos. No information was available regarding possible effects from terbufos manufacturing facilities. |
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Summary |
Value |
Study |
Safety factor |
|
ADI |
0-0.0006 mg/kg bw |
Rats and dogs, overall NOAEL for studies of repeated doses |
100 |
|
Acute RfD |
0.002 mg/kg bw |
Rat, study of acute neurotoxicity |
100 |
Dietary risk assessment
Long-term intake
The Meeting concluded that the long-term intake of residues of terbufos resulting from uses that have been considered by JMPR is unlikely to present a public health concern.