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EC number: 619-447-3 | CAS number: 99607-70-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Carcinogenicity
Administrative data
Description of key information
Not carcinogenic, 2-year feeding study in the rat (OECD TG 451, Fankhauser 1992)
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 20 March 1989 to 08 April 1991
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 451 (Carcinogenicity Studies)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 83-5 (Combined Chronic Toxicity / Carcinogenicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Japan, 59 Nohsan No. 4200
- Deviations:
- no
- GLP compliance:
- yes
- Species:
- rat
- Strain:
- other: Tif: RAIf (SPF)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: approximately 5 weeks
- Weight at week -1: 74.85-115.4 g (males), 76.33-107.4 g (females)
- Housing: 5 per sex in macrolon type 4 cages
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 11 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22±2°C
- Humidity: 55±10%
- Air changes: 16-20 per hr
- Photoperiod: 12 hrs dark / 12 hrs light
IN-LIFE DATES: From: 20 March 1989 To: 08 April 1991 - Route of administration:
- oral: feed
- Vehicle:
- other: diet
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): every 4 weeks
- Mixing appropriate amounts with (Type of food): certified standard diet (Nafag No. 890 Tox)
- Storage temperature of food: room temperature
VEHICLE
- Justification for use and choice of vehicle (if other than water): not applicable - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Pretest analyses confirmed stability of the diet preparations at room temperature over 35 days. The analysis of the first batch showed that food mixes were homogeneous (-9% to +7% of mean value). The analytically determined concentrations generally ranged from 84.8 to 104.6% of the nominal concentrations. The mean concentrations were 94.2%, 95.6 %, 93.0% and 93.2% of the nominal values in groups 2 to 5, respectively. The analytical data thus indicated that the mixing procedure was adequate and that the variance between nominal and actual dosage was generally acceptable.
- Duration of treatment / exposure:
- Two years
- Frequency of treatment:
- Continuous in diet
- Post exposure period:
- Not applicable
- Dose / conc.:
- 10 ppm
- Remarks:
- 0.43 mg/kg bw/day in females, 0.37 mg/kg bw/day in males
- Dose / conc.:
- 100 ppm
- Remarks:
- 4.33 mg/kg bw/day in females, 3.77 mg/kg bw/day in males
- Dose / conc.:
- 1 000 ppm
- Remarks:
- 41 mg/kg bw/day in females, 36 mg/kg bw/day in males
- Dose / conc.:
- 2 000 ppm
- Remarks:
- 82 mg/kg bw/day in females, 73 mg/kg bw/day in males
- No. of animals per sex per dose:
- 80 per sex per group;
50 animals per sex/group for carcinogenicity evaluation;
10 animals for clinical chemistry, haematology and urinalysis;
10 additional animals for haematology only;
10 animals for interim sacrifice after 12 months - Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: based on the results of previous acute and repeat dose studies
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily for signs of toxicity and mortality
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: at least weekly
BODY WEIGHT: Yes
- Time schedule for examinations: pretest and weekly during the first three months. Thereafter, the weight was recorded monthly
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean diet consumption calculated as g food/kg body weight/week: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
- Food consumption per cage were recorded pretest and weekly during the first three months. Thereafter, the weight was recorded monthly
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: Yes
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes
- Time schedule for examinations: monthly
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule/dose groups for examinations: eye examinations were conducted in control and high dose group animals pretest, after 26, 52, 78 weeks and at the end of the treatment period. Males and females from intermediate groups were examined prior to terminal sacrifice
HAEMATOLOGY: Yes
- Time schedule for collection of blood: after 13, 26, 52, 78 and 105 weeks
- Anaesthetic used for blood collection: Yes (ether)
- Animals fasted: Yes
- How many animals: 20/sex/group
- Parameters examined: erythrocyte count, haemoglobin, haematocrit, mean corpuscular volume, mean corpuscular haemoglobin, leucocyte count, differential leucocyte count, thrombocyte count, prothrombin time, red cell morphology
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: after 13, 26, 52, 78 and 105 weeks
- Anaesthetic used for blood collection: Yes (ether)
- Animals fasted: Yes
- How many animals: 10/sex/group
- Parameters examined: glucose, urea, creatinine, total bilirubin, total protein, albumin, globulins, A/G ratio, cholesterol, sodium, potassium, calcium, chloride, inorganic phosphorus, aspartate aminotransferase, alanine aminotransferase, alkaline phosphatase, gamma-glutamyl transpeptidase
URINALYSIS: Yes
- Time schedule for collection of urine: pretest and after 13, 26, 52, 78 and 104 weeks
- Metabolism cages used for collection of urine: Yes
- Animals fasted: Yes (no access to food or water)
- Parameters examined: volume, colour, relative density, pH, protein, glucose, ketones, bilirubin, blood, urobilinogen, urine sediment
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (all animals)
- the following organs were weighed: brain, liver, kidneys, adrenals, gonads, spleen (after one year of treatment). At the end of the 2 year period, the thyroid and pituitary glands were also weighed
HISTOPATHOLOGY: Yes (all animals)
- the following tissues were examined microscopically: skin, mammary area, spleen, mesenteric lymph node, axillary lymph node, sternum with bone marrow, femur with joint, skeletal muscle, trachea, lung, heart, aorta, submandibular salivary gland, liver, pancreas, oesophagus, stomach, small intestine, large intestine, kidneys, urinary bladder, prostate, seminal vesicle, testis, epididymis, uterus, ovary, pituitary gland, adrenal gland, thyroid with parathyroid gland, thymus, peripheral nerve, brain, spinal cord, eye with optic nerve, extraorbital lacrimal gland, any tissue with gross lesions - Other examinations:
- At autopsy, fat samples were taken to investigate the accumulation of cloquintocet-mexyl after 12 and 24 months.
- Statistics:
- Univariate standard methods were applied to the data. Each group was compared to controls by Lepage’s two sample test and tested for trends by Jonckheere’s test for ordered alternatives.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Food consumption was markedly depressed in the high dose group males during the first week of the treatment. Thereafter consumption was similar to that of the control animals throughout the treatment period. The overall food intake of treated groups was within 1.6% of that of the relative controls.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Histopathology did not reveal any inflammatory or degenerative changes which could be related to the test article. Lymphoid hyperplasia of the thymus was diagnosed in some males. The statistical trend analysis indicated a significant, treatment-related effect in the top dose group. There was no effect on thymic neoplastic lesions.
Among the females, increased incidences of thyroid gland follicle hyperplasia were found. The changes were graded as slight in all cases with no dose-related trend in severity. Statistical analysis indicated a significant effect in the animals treated at 1000 ppm and above. Hyperplasia of the thyroid follicle epithelium is known to occur spontaneously in the rat strain used and the incidence in the 100 ppm dose group was comparable to the incidence usually found in control animals of this rat strain. In the absence of a dose relationship, the observation made in the 10 ppm group was considered to be an outlier and thus incidental. Furthermore there was no correlation between thyroid hyperplasia and proliferative lesions of the pituitary gland. Incidences of thyroid tumours were within the historical control range, indicating that there was no progression of the hyperplasia to neoplastic growth. - Histopathological findings: neoplastic:
- no effects observed
- Description (incidence and severity):
- The incidence of all neoplasms were within the historical control range of the rat strain used and not considered to have been influenced by the treatment.
Cloquintocet-mexyl was devoid of a carcinogenic activity in the rat. The total number of tumour bearing animals and of animals with multiple tumours were similar in all groups - Relevance of carcinogenic effects / potential:
- The treatment had no influence on the spontaneous tumour profile of the rat strain used and thus it is concluded that cloquintocet-mexyl is not carcinogenic in the rat.
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 2 000 ppm (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No treatment-related effects on the spontaneous tumour profile at the highest dose tested (2000 ppm; 73/82 mg/kg bw/day).
- Conclusions:
- There were no treatment-related effects on the spontaneous tumour profile and it is concluded that 2000 ppm cloquintocet-mexyl is a NOEL for carcinogenicity in the rat.
- Executive summary:
The carcinogenicity of the substance in the rat was studied under GLP to OECD TG 451. Groups of 80 male and 80 female Tif:RAIf (SPF) rats were fed diet containing 0 (control), 10, 100, 1000 or 2000 ppm cloquintocet-mexyl. Mortality, clinical appearance and behaviour, bodyweights, bodyweight changes, food consumption, ophthalmology, haematology, blood and urine biochemistry, organ weights, gross pathology and histopathology were assessed. Ten animals per group per sex were killed after 52 weeks of treatment for interim examination.
Cloquintocet-mexyl was well tolerated at dietary concentrations up to 2000 ppm (73.4/81.5 mg/kg bwt/day in males and females respectively). The effects of toxicological significance were hyperplasic changes in the thymus of males treated at 2000 ppm and of the thyroid gland in females treated at 1000 and 2000 ppm. The treatment had no influence on the spontaneous tumour profile of the rat strain used and thus it is concluded that cloquintocet-mexyl is not carcinogenic in the rat.
Based on the histopathological findings of the thyroid follicular epithelial hyperplasia at 1000 ppm in females the NOAEL for systemic toxicity was 100 ppm, equivalent to a mean daily dose of 3.77/4.33 mg/kg bw/day in males and females respectively.
Reference
Table 2: Test compound consumption: The average test article intake based on nominal and actual dietary concentrations
Dose of test material |
Test article intake (based on nominal concentrations) |
Test article intake (based on actual concentrations) |
10 ppm |
m: 0.387 mg/kg |
m: 0.365 mg/kg |
100 ppm |
m: 3.947 mg/kg |
m: 3.773 mg/kg |
1000 ppm |
m: 39.10 mg/kg |
m: 36.36 mg/kg |
2000 ppm |
m: 78.56 mg/kg |
m: 73.40 mg/kg |
Table 3: Cloquintocet-mexyl – 24-month rat study - Survival
% survival after 104 weeks |
0 |
10 |
100 |
1000 |
2000 |
Males Females |
52% 56% |
46% 58% |
42% 62% |
26% 42% |
46% 58% |
Table 4: Histopathological findings in the chronic rat study with cloquintocet-mexyl
0 |
10 |
100 |
1000 |
2000 |
Historic control values |
|
Males |
||||||
Thymus - Lymphoid hyperplasia - severity |
0 |
0 |
1 1 |
2 1 |
5 2 |
|
- Lymphoma |
0 |
2 |
0 |
1 |
0 |
|
Thyroid - hyperplasia follicular epithelium |
2 |
6 |
7 |
5 |
3 |
|
- adenoma |
4 |
1 |
1 |
4 |
3 |
|
- carcinoma |
1 |
0 |
2 |
0 |
1 |
|
Females |
||||||
Thymus - Lymphoid hyperplasia |
2 |
2 |
0 |
0 |
0 |
|
Thyroid - hyperplasia follicular epithelium - severity |
0 0 |
8 1.4 |
5 1.6 |
10 1.5 |
11 1.4 |
0-4/76 |
- adenoma |
0 |
1 |
2 |
0 |
2 |
0-3/77 |
- carcinoma |
0 |
0 |
0 |
1 |
2 |
2/77 |
Table 5: Occurrence of primary tumours in the chronic rat study with cloquintocet-mexyl
males |
females |
|||||||||
ppm |
0 |
10 |
100 |
1000 |
2000 |
0 |
10 |
100 |
1000 |
2000 |
Number of tumour-bearing animals |
55 |
48 |
51 |
55 |
56 |
60 |
63 |
63 |
59 |
63 |
Number of animals with one tumour |
28 |
25 |
32 |
28 |
31 |
31 |
36 |
37 |
34 |
35 |
Number of animals with two tumours |
17 |
18 |
13 |
19 |
19 |
22 |
21 |
19 |
19 |
22 |
Number of animals with three tumours |
6 |
3 |
4 |
7 |
4 |
6 |
4 |
6 |
5 |
5 |
Number of animals with four tumours |
0 |
2 |
1 |
1 |
0 |
1 |
2 |
1 |
1 |
1 |
Number of animals with five tumours |
3 |
0 |
1 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 73 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
- Quality of whole database:
- A fully reliable GLP 24-months chronic feeding study in the rat is available. This is supported by a fully reliable 80-weeks feeding study in mice.
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Cloquintocet-mexyl is considered not to be carcinogenic and no classification is warranted under Regulation (EC) 1272/2008, Annex I, Part 3, 3.6.2.
Additional information
Dietary studies in rats (Fankhauser 1992) and mice (Fankhauser 1992) have been performed. No evidence of carcinogenicity was seen at the highest dose tested in either species. In rats, hyperplastic changes were seen in the thymus of males at 2000 ppm and of the thyroid gland in the females at 1000 and 2000 ppm. Dietary administration to mice over 18 months resulted in reduced body weights in both sexes, lower food consumption in females, increased water consumption in both sexes and chronic inflammatory changes in the urinary bladder in males at 5000 ppm. No statistically significant treatment-related increase in any tumour type was seen in either study.
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