Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 604-636-5 | CAS number: 148477-71-8
- 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
Endpoint summary
Administrative data
Description of key information
The Key Studies for the repeated dose toxicity endpoint are as follows:
90-day oral (dietary) rat study (M-005766-02-1)
12-month oral (dietary) dog study (M-045424-02-1)
28-day dermal toxicity study in the rat (M-011043-01-1)
A number of Supporting Studies are also available:
28-day oral (dietary) rat study (M-024721-01-1)
28-day oral (dietary) dog study (M-027510-02-1)
8-week investigative oral (dietary) dog study (M-052495-01-1)
90-day oral (dietary) mouse study (M-005729-03-1)
90-day oral (dietary) dog study (M-032514-02-1)
Non-standard 19-week oral (dietary) rat study (M-049165-01-1)
Chronic toxicity/carcinogenicity studies are also available in the rat (M-026284-02-1) and in the mouse (M-044116-01-1).
The lowest NOAEL (1.45 mg/kg bw/d) is reported in the 12-month oral (dietary) dog study (M-045424-02-1); however, the mouse chronic toxicity/carcinogenicity study does not identify a NOAEL (LOAEL =4.1 mg/kg bw/d).
Key value for chemical safety assessment
- Toxic effect type:
- dose-dependent
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 452 (Chronic Toxicity Studies)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.4100 (Chronic Toxicity)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Species:
- dog
- Strain:
- Beagle
- Details on species / strain selection:
- Standard laboratory species/strain
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- 40 purebred beagles (20 males, 20 nulliparous non-pregnant females) from the breeder Harlan-Winkelmann were used in the study. After an acclimatization period, dogs judged to be healthy both clinically and on the basis of the laboratory data from the screening investigation (from a total group of 25 males and 25 females) were randomly assigned to groups after prior stratification for sex and body weight. In week -1 the dogs were 33 - 37 weeks old and weighed between 10.4 and 15.7 kg. During acclimatization and the conduct of the study all the male
and female beagles were housed in individual cages (floor area approximately 1.10 x 1.15 m) in a room reserved for the sole use of the present study. The room was force-ventilated. The temperature, which was recorded, was predominantly 19.0 - 26.0° C during the study. The average atmospheric humidity was approximately 17 - 95 %. Brief fluctuations in the environmental conditions (temperature, humidity), that could occur, for example, when the room and the cages were being spray-cleaned, had no clinically discernible influence on the health of the animals. The premises were illuminated by diffuse daylight (skylights), but mainly by fluorescent lamps, which regulated the day/night cycle automatically (12 h day and 12 h night). Except on weekends and on public holidays all animals, separated according to sex, were allowed to exercise daily for at least 60 min - generally in the morning - in a special room directly
connected to the animal room. - Route of administration:
- oral: feed
- Details on route of administration:
- Test material was mixed with feed at different concentrations and consumed daily.
- Vehicle:
- unchanged (no vehicle)
- Remarks:
- The test material was administered in the diet
- Details on oral exposure:
- Groups of 4 male and 4 female Beagle dogs were treated orally over a period of about 52 weeks with daily concentrations of 0 (control group), 20, 50, 150 and 600 ppm spirodiclofen in their diet. The highest dose group was initially treated with 500 ppm until study week 4, after which this dose group received 600 ppm in agreement with EPA.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Before starting the study, it had been found out that the feed/substance mix was not stable over a period of 7 days. The analytical data verify that the test material in the animal ration was homogeneously distributed within the concentration range of 400 ppm to 10000 ppm. Under current sample preparation and handling conditions comparable to those in the actual study the chemical stability was assured for a period of at least 4 days. The stability in moist animal feed within the concentration range of 100 ppm to 10000 ppm was assured for a period of at least 5 hours. In addition, stability in moist feed was assured for the concentrations of 20 and 50 ppm for at least 2 hours.
- Duration of treatment / exposure:
- 52 weeks
- Frequency of treatment:
- Daily
- Dose / conc.:
- 0 ppm
- Remarks:
- Controls
- Dose / conc.:
- 20 ppm
- Remarks:
- Equivalent to a mean intake of 0.57 mg/kg bw/d (sexes combined)
- Dose / conc.:
- 50 ppm
- Remarks:
- Equivalent to a mean intake of 1.45 mg/kg bw/d (sexes combined)
- Dose / conc.:
- 150 ppm
- Remarks:
- Equivalent to a mean intake of 4.54 mg/kg bw/d (sexes combined)
- Dose / conc.:
- 600 ppm
- Remarks:
- Equivalent to a mean intake of 16.9 mg/kg bw/d (sexes combined)
- No. of animals per sex per dose:
- Groups of 4 male and 4 females per dose
- Control animals:
- yes, plain diet
- Details on study design:
- Groups of 4 male and 4 female Beagle dogs were treated orally over a period of about 52 weeks with daily concentrations of 0 (control group), 20, 50, 150 and 600 ppm spirodiclofen in their diet. The highest dose group was initially treated with 500 ppm until study week 4, after which this dose group received 600 ppm in agreement with EPA. The test substance intakes over the whole study period were 0.57, 1.45, 4.54, 16.9 mg/kg bw/day (mean values for both sexes). The animals were observed daily for clinical signs. Testing of reflexes (pupillary, corneal, patellar, extensor, postural and flexor), body temperature, pulse rate and heart rate, and ECG determinations were performed in weeks -3, 6, 12, 26, 39 and 52 with the following exceptions: heart rates were performed in week 27 rather than week 26 and reflexes were not tested during the week 26/27 interval. Clinical chemistry and hematology measurements were done in weeks –3, -1, 3, 6, 12, 26, 39 and 52.
- Positive control:
- Not required for this study type.
- Observations and examinations performed and frequency:
- The animals were observed daily for clinical signs. Testing of reflexes (pupillary, corneal, patellar, extensor, postural and flexor), body temperature, pulse rate and heart rate, and ECG determinations were performed in weeks -3, 6, 12, 26, 39 and 52 with the following exceptions: heart rates were performed in week 27 rather than week 26 and reflexes were not tested during the week 26/27 interval.
- Sacrifice and pathology:
- Clinical chemistry and hematology measurements were done in weeks –3, -1, 3, 6, 12, 26, 39 and 52.
- Clinical signs:
- no effects observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- The clinical chemical investigations revealed a slight increase of transaminase activities (ALT, AST) in the 600 ppm males and females but also in control animals beginning in study week 6 so that a treatment-relationship is not obvious. Cholesterol levels were slightly decreased at 600 ppm in both sexes in week 6 and 12.
- Endocrine findings:
- not examined
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- Increased relative organ weights of testes and prostates in 150 and 600 ppm males and of the adrenal glands in 600 ppm females were observed
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Histopathology revealed minimal or slight Leydig cell vacuolation in the testes of all animals dosed at 600 ppm and in one male of this group also slight Leydig cell hypertrophy. In one male from this group a bilateral slight tubular degeneration was observed.
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- Evidence of microsomal liver enzyme induction was seen at 600 ppm. Slight elevations of NDE were also seen at lower doses but ODE was only increased at 600 ppm. Since no hepatocellular hypertrophy as a morphological correlate of liver enzyme induction occurred at any dose this response is regarded as equivocal or borderline effect.
- Details on results:
- General observations: No clinical signs were observed, and all animals survived the study period. Determinations of reflexes, body temperature, pulse rate and heart rate did not reveal substance-induced changes. Also the ECG measurements and the ophthalmoscopic examinations did not indicate treatment-related effects. No significant differences could be observed regarding the nutritional state of the animals. Feed intake was not impaired by the treatment in any dose groups, an incomplete feed intake in the initial study phase occurred in all groups without a dose-relationship. Based on the dietary consumption, the test compound intake was calculated. Body weight development was normal in all treatment groups as compared to the control group.
Hematology, clinical chemistry, urinalysis: Hematological investigations did not reveal any remarkable differences between control and test animals. The clinical chemical investigations revealed a slight increase of transaminase activities (ALT, AST) in the 600 ppm males and females but also in control animals beginning in study week 6 so that a treatment-relationship is not obvious. Cholesterol levels were slightly decreased at 600 ppm in both sexes in week 6 and 12. Urinalysis did not reveal any changes between control and treated animals.
Evidence of microsomal liver enzyme induction was seen at 600 ppm. Slight elevations of NDE were also seen at lower doses but ODE was only increased at 600 ppm. Since no hepatocellular hypertrophy as a morphological correlate of liver enzyme induction occurred at any dose this response is regarded as equivocal or borderline effect Gross pathology, organ weights, histopathology: At necropsy no evidence of any gross pathological findings related to treatment with the test compound was found. Increased relative organ weights of testes and prostates in 150 and 600 ppm males and of the adrenal glands in 600 ppm females were observed. Histopathology revealed minimal or slight Leydig cell vacuolation in the testes of all animals dosed at 600 ppm and in one male of this group also slight Leydig cell hypertrophy. In one male from this group a bilateral slight tubular degeneration was observed. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 50 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- histopathology: non-neoplastic
- Remarks on result:
- other: adrenal effects (vacuolization
- Key result
- Critical effects observed:
- no
- Lowest effective dose / conc.:
- 50 ppm
- Organ:
- adrenal glands
- Conclusions:
- The NOAEL of 50 ppm (equivalent to 1.38 mg/kg bw/d in males and of 1.52 mg/kg bw/d in females) was based on adrenal effects (vacuolization) at 150 ppm.
- Executive summary:
Groups of 4 male and 4 female Beagle dogs were treated with spirodiclofen orally over a period of 52 weeks using dietary concentrations of 0 (control group), 20, 50, 150 and 600 ppm. The highest dose group was initially treated with 500 ppm until study week 4, after which this dose group received 600 ppm. The test substance intakes over the whole study period were 0.57, 1.45, 4.54, 16.9 mg/kg bw/d (mean values for both sexes). The animals were daily observed for clinical signs. Testing of reflexes (pupillary, corneal, patellar, extensor, postural and flexor), body temperature, pulse rate and heart rate and ECG determinations were performed in weeks -3, 6, 12, 26, 39 and 52. Clinical chemistry and hematology measurements were done in weeks –3, -1, 3, 6, 12, 26, 39 and 52. No clinical signs were observed, and all animals survived the study period. Determinations of reflexes, body temperature, pulse rate and heart rate did not reveal substance-induced changes. ECG measurements and the ophthalmoscopic examinations did not indicate treatment-related effects. No significant differences could be observed regarding the nutritional state of the animals. Feed intake was not impaired by the treatment in any dose groups, an incomplete feed intake in the initial study phase occurred in all groups without a dose-relationship. Body weight development was normal in all treatment groups as compared to the control group. Hematological investigations did not eveal any remarkable differences between control and test animals. The clinical chemical investigations revealed a slight increase of transaminase activities (ALT, AST) in the 600 ppm males and females but also in control animals beginning in study week 6 so that a treatment-relationship is not obvious. Cholesterol levels were slightly decreased at 600 ppm in both sexes in week 6 and 12. Urinalysis did not reveal any changes between control and treated animals. Evidence of microsomal liver enzyme induction was seen at 600 ppm. Slight elevations of NDE were also seen at lower doses but ODE was only increased at 600 ppm. Since no hepatocellular hypertrophy as a morphological correlate of liver enzyme induction occurred at any dose this response is regarded as equivocal or borderline effect. At necropsy, no evidence of any gross pathological findings related to treatment was found. Increased relative organ weights of testes and prostates in 150 and 600 ppm males and of the adrenal glands in 600 ppm females were observed. Histopathology revealed minimal or slight Leydig cell vacuolation in the testes of all animals dosed at 600 ppm and in one male of this group also slight Leydig cell hypertrophy. In one male from this group a bilateral slight tubular degeneration was observed. The NOAEL of 50 ppm (equivalent to 1.38 mg/kg bw/d in males and of 1.52 mg/kg bw/d in females) was based on adrenal effects (vacuolization) at 150 ppm.
Reference
Chronic toxicity dog study: Clinical Chemistry (males)
Week | AST (U/L) | ALT(U/L) | Chol(mmol/L) |
0ppm | |||
-3 | 11.0 | 17.5 | 3.93 |
-1 | 11.0 | 19.1 | |
3 | 11.7 | 20.1 | 3.29 |
6 | 13.4 | 19.1 | 3.16 |
12 | 14.9 | 19.8 | 2.75 |
26 | 13.4 | 24.5 | 3.26 |
39 | 12.0 | 37.6 | 3.55 |
52 | 18.6 | 29.7 | 3.28 |
20 ppm | |||
-3 | 10.4 | 16.4 | 4.62 |
-1 | 11.2 | 15.4 | |
3 | 12.6 | 20.2 | 3.75 |
6 | 18.0 | 26.3 | 3.13 |
12 | 13.5 | 18.8 | 3.30 |
26 | 13.6 | 23.2 | 4.26 |
39 | 12.7 | 21.2 | 4.54 |
52 | 15.0 | 26.3 | 4.82 |
50ppm | |||
-3 | 11.6 | 17.2 | 4.84 |
-1 | 10.5 | 15.6 | |
3 | 14.5 | 20.1 | 3.79 |
6 | 14.2 | 17.4 | 3.62 |
12 | 12.6 | 19.1 | 3.90 |
26 | 13.9 | 20.1 | 4.07 |
39 | 13.8 | 21.3 | 4.20 |
52 | 14.3 | 21.4 | 4.09 |
Chronic toxicity dog study: Clinical Chemistry (females)
week | AST | ALT | Chol |
0mm | |||
-3 | 12.3 | 14.8 | 3.93 |
-1 | 10.2 | 13.0 | |
3 | 11.9 | 13.6 | 3.88 |
6 | 12.8 | 20.6 | 3.16 |
12 | 15.3 | 20.1 | 2.73 |
26 | 14.8 | 24.6 | 4.39 |
39 | 11.1 | 83.5 | 5.90 |
52 | 11.0 | 16.0 | 5.89 |
20ppm | |||
-3 | 12.3 | 15.8 | 3.76 |
-1 | 10.6 | 14.3 | |
3 | 11.1 | 15.4 | 3.18 |
6 | 19.4 | 18.0 | 2.77 |
12 | 12.4 | 17.0 | 3.33 |
26 | 15.3 | 20.5 | 4.81 |
39 | 10.6 | 16.5 | 4.31 |
52 | 12.2 | 16.0 | 4.58 |
50ppm | |||
-3 | 13.9 | 19.5 | 4.09 |
-1 | 12.7 | 16.8 | |
3 | 17.2 | 22.5 | 3.26 |
6 | 25.1 | 25.2 | 2.73 |
12 | 14.4 | 20.3 | 3.08 |
26 | 15.8 | 18.9 | 3.88 |
39 | 11.7 | 18.4 | 4.75 |
52 | 13.4 | 18.5 | 4.09 |
Chronic toxicity dog study: Clinical Chemistry (females) (continued)
week | AST | ALT | Chol |
150ppm | |||
-3 | 13.7 | 18.6 | 4.12 |
-1 | 12.1 | 17.2 | |
3 | 14.7 | 18.5 | 3.05 |
6 | 16.9 | 21.0 | 2.82 |
12 | 14.1 | 18.8 | 2.87 |
26 | 13.3 | 22.1 | 3.47 |
39 | 12.0 | 20.0 | 3.57 |
52 | 12.7 | 17.2 | 5.54 |
600ppm | |||
-3 | 12.4 | 16.3 | 3.99 |
-1 | 11.4 | 15.5 | |
3 | 15.7 | 16.7 | 3.07 |
6 | 20.5 | 28.1 | 2.67 |
12 | 15.6 | 21.7 | 3.04 |
26 | 15.9 | 20.5 | 4.21 |
39 | 13.2 | 18.9 | 4.44 |
52 | 14.0 | 18.9 | 4.77 |
Chronic study in dogs: microsomal liver enzyme activities (both sexes)
Liver enzymes | Dose (ppm) | ||||
0 | 20 | 50 | 150 | 600 | |
N-DEM (1) | 71.1 | 73.7 | 85.5 | 100.1* | 144.00** |
0-DEM (1) | 20.4 | 20.1 | 23.2 | 23.7 | 32.2 |
P450 (2) | 27.6 | 27.3 | 29.8 | 30.1 | 34.4* |
1 mU/g
2 nmol/g
Chronic toxicity dog study: Relative organ weights (g/kg bw)
Dose (ppm) | 0 | 20 | 50 | 150 | 600 |
Males | |||||
Testes | 1.38 | 1.64 | 1.44 | 1.77 | 1.79 |
Prostate | 0.70 | 0.71 | 0.72 | 0.73 | 0.83 |
Females | |||||
Adrenals | 0.131 | 0.140 | 0.130 | 0.145 | 0.154 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 1.45 mg/kg bw/day
- Study duration:
- chronic
- Species:
- dog
- Quality of whole database:
- A comprehensive and high-quality database of repeated dose oral toxicity studies of up to chronic duration are available for the rat, mouse and dog. A sub-acute dermal toxicity study is also available for the rat. The key studies are GLP- and guideline-compliant; the supporting studies include guideline-compliant and non-guideline investigative studies.
- System:
- endocrine system
- Organ:
- adrenal glands
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 9 February 1998 to 4 May 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: 67/548/EEC
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.9 (Repeated Dose (28 Days) Toxicity (Dermal))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3200 (Repeated Dose Dermal Toxicity -21/28 Days)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 410 (Repeated Dose Dermal Toxicity: 21/28-Day Study)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- Standard laboratory species/strain with background control data available
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Winkelmann GmbH
- Females nulliparous and non-pregnant: yes
- Age at study initiation: 7-8 weeks
- Weight at study initiation: 223-250 g (M), 200-207 g (F)
- Fasting period before study: none
- Housing: individual
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least five days
DETAILS OF FOOD AND WATER QUALITY:
The rations consisted of fixed-formula standard diet (Altromin 1324 (= pelletized 1321) Diet for Rats and Mice) supplied by Altromin GmbH, and of tap water (drinking bottles). Feed and water were available ad libitum and were supplied in polycarbonate bottles and in stainless steel cage cover, respectively. The nutritive composition and the contaminant-content of the standard diet were routinely spot-checked and analyzed. The tap water complied with the German Drinking Water Ordinance.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18-22
- Humidity (%): 50-60
- Air changes (per hr): 15-20
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 18 February 1998 To: 17 March 1998 - Type of coverage:
- semiocclusive
- Vehicle:
- unchanged (no vehicle)
- Remarks:
- The test material was applied as a solid onto a wet gauze pad
- Details on exposure:
- Two days before the start of the treatment the back and flanks of the rats were shorn. Any regrowth of hair was shaved off the skin areas marked for treatment twice weekly. For each animal the required amount of test substance was weighed and transferred to the wet gauze-layer (5.5 x 5.5 cm = 30.25 cm2) of a sterile patch and placed on the rat's back. The gauze strip was secured in place using adhesive stretch tape (8 x 23 cm). Additionally, the mobility of the rats was impaired by a rat jacket. The gauze strip has the same size as the application area, i.e. 30.25 cm2. Thus, the application area was greater than 10% of the body surface area of the rat. After an exposure time of 6 hours the fixing bandage and the gauze strip were removed and the treated area cleaned with soap and water. Control animals were treated with tap water.
- Analytical verification of doses or concentrations:
- no
- Remarks:
- Analytical determinations of stability and homogeneity were not performed because the test substance was applied undiluted.
- Duration of treatment / exposure:
- The test material was applied for 6 hours/day
- Frequency of treatment:
- The test material was applied daily; 5 days/week for 28 days (total 22 applications). On the first three weeks of the study, the formulations were applied on 5 days per week, and in the fourth week also on Saturday and Sunday. Thus, both males and females were dosed daily over the final seven days prior to terminal sacrifice.
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- Control; water only
- Dose / conc.:
- 1 000 mg/kg bw/day
- Remarks:
- Test material moistened with water
- No. of animals per sex per dose:
- Groups of 5 male and 5 female rats per dose.
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Groups of 5 male and 5 female Wistar rats of the strain Hsd Cpb: WU were administered spirodiclofen, at levels of 0 and 1000 mg/kg bw/d by dermal application. Analytical determinations of stability and homogeneity were not performed because the test substance was applied undiluted and only moistened with water immediately before application. Males and females received 22 applications within a total period of 28 days. The exposure time per day was 6 hours. The doses were based on the results of a dose range finding study in female rats. In that study, the doses were 0 and 1000 mg/kg bw/d. The animals were treated 10 times during a period of 14 days. On the application area neither erythema nor edema of the skin were observed. The administration of 1000 mg/kg bw/d showed no toxicologically significant effects.
- Positive control:
- Not required for this study type
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least daily
DETAILED CLINICAL OBSERVATIONS: No
DERMAL IRRITATION: Yes
- Time schedule for examinations: at least daily
Erythema was scored using the Draize scale. The evaluation of swelling (in males and in females on days 0, 2, 6 ,9, 13, 16, 20, 23, 27) was done by measuring the skinfold thickness on the back in the center of the application area using a cutimeter or skinfold caliper. Measurements were taken at two different locations within the treatment area. From these a mean value was calculated
BODY WEIGHT: Yes
- Time schedule for examinations: Weekly
FOOD CONSUMPTION: Yes
- Time schedule for examinations: Weekly
FOOD EFFICIENCY: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
CBC Complete blood cell count
DIFF white blood cell differential
LEUCO Leucocytes
ERY Erythrocytes
HB Hemoglobin
HCT Hematocrit, calculated
MCV Mean Corpuscular Volume
MCH Mean Corpuscular Hemoglobin, calculated
MCHC Mean Corpuscular Hemoglobin Concentration, calculated
THRO Platelets/Thrombocytes
NEUTRO Neutrophils
LYMPH Lymphocytes
MONO Monocytes
EOS Eosinophils
BASO Basophils
ATYP Atypical Leucocytes
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: Glucose tests were carried out on relative day 27. Laboratory tests on blood samples were carried out at the end of the 4-week treatment period (relative day 28). Blood samples for glucose determination were taken from fasted, non-anesthetized animals. The blood was obtained from the distal vessels of the tail. The blood for the other tests was withdrawn from animals under deep diethyl ether anesthesia by heart puncture at the time of necropsy.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
ORGAN WEIGHTS: Yes
The following exsanguinated organs of the animals sacrificed at necropsy were weighed in the unfixed state: adrenal glands, brain, epididymides, heart, kidneys, liver, spleen, testes, thymus. The organ weights are specified in both absolute and relative terms. The relative organ weights were calculated by normalization to 100 g body weight (individual organ weight divided by body weight times 100). The body weight used as a basis for this calculation was determined immediately prior to necropsy of the pertinent animal.
HISTOPATHOLOGY: Yes - Statistics:
- The quantitative results for individual animals were used to calculate arithmetic group means and standard deviations. The results for the groups that received the test substance were compared with those for the control group and significant differences indicated by "+" for p<0.05 and "++" for p<0.01. In case of numbers of values too low to calculate test statistics this is indicated by "nc".
The Dunnett test was used for body weight, body weight gain, feed consumption and organ weight data (relative organ weights subsequent to logarithmic transformation).. - Clinical signs:
- no effects observed
- Description (incidence and severity):
- No systemic clinical signs were observed
- Dermal irritation:
- no effects observed
- Description (incidence and severity):
- Skin reddening was not observed either in the control or in the dose group. During the entire treatment period, the mean skinfold thickness of the 1000 mg/kg group animals was comparable to the controls.
- Mortality:
- no mortality observed
- Description (incidence):
- No animal died throughout the entire treatment period.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- In males and in females, the body weights and the body weight development were not impaired. Through the entire study, in females at 1000 mg/kg bw/d, the body weights were slightly higher than in the controls.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- In male and in female animals, the food consumption per animal was unaffected by treatment. In males, at day 7 a very slight decrease of the daily feed intake per kg body weight was calculated. This statistically significant effect is regarded as incidental.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- There were no effects of treatment observed, neither on red blood cells, nor on leucocyte counts, on hemogram, or on blood coagulation. The statistically significantly decreased hemoglobin and hematocrit values in males are considered incidental. These effects were observed only in one sex, no individual values in the dose group are below the lower limit of the biological range for animals of this age. Additionally, the control values are very high, they exceed the 2s range.
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- There were no toxicologically significant changes in clinical chemical parameters. The observed statistically significant differences of the activity of alanine aminotransferase and of the concentration of triglycerides and creatinine in males, as well as of the concentration of inorganic phosphate in females are considered incidental. These effects were observed only in one sex, and all individual values are in the biological range for animals of this age.
- Endocrine findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- No significant differences to the controls were observed.
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- There were no local or systemic histopathological findings attributable to the test substance in the organs/tissues examined.
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
- Description (incidence and severity):
- Skin reactions
- Details on results:
- Regarding survival rate, state of health, or general behavior of the animals there was no difference between the treated and untreated animals. At 1000 mg/kg no macro- or microscopical skin findings were observed. At 1000 mg/kg the feed consumption and the body weights did not differ
lexicologically significantly from those in the controls. Hematology tests afforded no evidence for a treatment-related effect at 1000 mg/kg. Neither the hematopoetic system nor the red and white blood cell populations or blood coagulation were affected. The results of clinical laboratory tests, gross pathology, organ gravimetry and histopathology afforded no evidence for a treatment-related effect. - Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Systemic toxicity
- Effect level:
- 1 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Local effects
- Effect level:
- 1 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- A 28-day dermal toxicity study in the rat was performed at the limit dose of 1000 mg/kg bw/d. A NOAEL of1000 mg/kg bw/d is reported for local and systemic effects.
- Executive summary:
In this sub-acute repeated dose toxicity study, groups of 5 male and 5 female Wistar rats were administered spirodiclofen at dose levels of 0 (controls) and 1000 mg/kg bw/d by dermal application. Analytical determinations of stability and homogeneity were not performed because the test substance was applied undiluted and only moistened with water immediately before application. Males and females received 22 applications within a total period of 28 days. The exposure time per day was 6 hours. General observations: No effects on body weight development, food consumption, clinical signs, or skin reactions were seen. Clinical chemistry and hematology did not reveal any treatment-related changes. The results of gross pathology, organ weight analysis and histopathology did not reveal evidence of a treatment-related effect. In conclusion, neither systemic nor local skin effects were observed after a dermal administration of 1000 mg/kg bw/d to rats for four weeks. 1000 mg/kg bt/d is therefore regarded as the NOAEL for local and systemic effects in male and female rats.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Experimental exposure time per week (hours/week):
- 30
- Species:
- rat
- Quality of whole database:
- A GLP- and guideline compliant 28-day dermal toxicity study in the rat (Klimisch =1) is available
Repeated dose toxicity: dermal - local effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 9 February 1998 to 4 May 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: 67/548/EEC
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.9 (Repeated Dose (28 Days) Toxicity (Dermal))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3200 (Repeated Dose Dermal Toxicity -21/28 Days)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 410 (Repeated Dose Dermal Toxicity: 21/28-Day Study)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- Standard laboratory species/strain with background control data available
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Winkelmann GmbH
- Females nulliparous and non-pregnant: yes
- Age at study initiation: 7-8 weeks
- Weight at study initiation: 223-250 g (M), 200-207 g (F)
- Fasting period before study: none
- Housing: individual
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least five days
DETAILS OF FOOD AND WATER QUALITY:
The rations consisted of fixed-formula standard diet (Altromin 1324 (= pelletized 1321) Diet for Rats and Mice) supplied by Altromin GmbH, and of tap water (drinking bottles). Feed and water were available ad libitum and were supplied in polycarbonate bottles and in stainless steel cage cover, respectively. The nutritive composition and the contaminant-content of the standard diet were routinely spot-checked and analyzed. The tap water complied with the German Drinking Water Ordinance.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18-22
- Humidity (%): 50-60
- Air changes (per hr): 15-20
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 18 February 1998 To: 17 March 1998 - Type of coverage:
- semiocclusive
- Vehicle:
- unchanged (no vehicle)
- Remarks:
- The test material was applied as a solid onto a wet gauze pad
- Details on exposure:
- Two days before the start of the treatment the back and flanks of the rats were shorn. Any regrowth of hair was shaved off the skin areas marked for treatment twice weekly. For each animal the required amount of test substance was weighed and transferred to the wet gauze-layer (5.5 x 5.5 cm = 30.25 cm2) of a sterile patch and placed on the rat's back. The gauze strip was secured in place using adhesive stretch tape (8 x 23 cm). Additionally, the mobility of the rats was impaired by a rat jacket. The gauze strip has the same size as the application area, i.e. 30.25 cm2. Thus, the application area was greater than 10% of the body surface area of the rat. After an exposure time of 6 hours the fixing bandage and the gauze strip were removed and the treated area cleaned with soap and water. Control animals were treated with tap water.
- Analytical verification of doses or concentrations:
- no
- Remarks:
- Analytical determinations of stability and homogeneity were not performed because the test substance was applied undiluted.
- Duration of treatment / exposure:
- The test material was applied for 6 hours/day
- Frequency of treatment:
- The test material was applied daily; 5 days/week for 28 days (total 22 applications). On the first three weeks of the study, the formulations were applied on 5 days per week, and in the fourth week also on Saturday and Sunday. Thus, both males and females were dosed daily over the final seven days prior to terminal sacrifice.
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- Control; water only
- Dose / conc.:
- 1 000 mg/kg bw/day
- Remarks:
- Test material moistened with water
- No. of animals per sex per dose:
- Groups of 5 male and 5 female rats per dose.
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Groups of 5 male and 5 female Wistar rats of the strain Hsd Cpb: WU were administered spirodiclofen, at levels of 0 and 1000 mg/kg bw/d by dermal application. Analytical determinations of stability and homogeneity were not performed because the test substance was applied undiluted and only moistened with water immediately before application. Males and females received 22 applications within a total period of 28 days. The exposure time per day was 6 hours. The doses were based on the results of a dose range finding study in female rats. In that study, the doses were 0 and 1000 mg/kg bw/d. The animals were treated 10 times during a period of 14 days. On the application area neither erythema nor edema of the skin were observed. The administration of 1000 mg/kg bw/d showed no toxicologically significant effects.
- Positive control:
- Not required for this study type
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least daily
DETAILED CLINICAL OBSERVATIONS: No
DERMAL IRRITATION: Yes
- Time schedule for examinations: at least daily
Erythema was scored using the Draize scale. The evaluation of swelling (in males and in females on days 0, 2, 6 ,9, 13, 16, 20, 23, 27) was done by measuring the skinfold thickness on the back in the center of the application area using a cutimeter or skinfold caliper. Measurements were taken at two different locations within the treatment area. From these a mean value was calculated
BODY WEIGHT: Yes
- Time schedule for examinations: Weekly
FOOD CONSUMPTION: Yes
- Time schedule for examinations: Weekly
FOOD EFFICIENCY: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
CBC Complete blood cell count
DIFF white blood cell differential
LEUCO Leucocytes
ERY Erythrocytes
HB Hemoglobin
HCT Hematocrit, calculated
MCV Mean Corpuscular Volume
MCH Mean Corpuscular Hemoglobin, calculated
MCHC Mean Corpuscular Hemoglobin Concentration, calculated
THRO Platelets/Thrombocytes
NEUTRO Neutrophils
LYMPH Lymphocytes
MONO Monocytes
EOS Eosinophils
BASO Basophils
ATYP Atypical Leucocytes
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: Glucose tests were carried out on relative day 27. Laboratory tests on blood samples were carried out at the end of the 4-week treatment period (relative day 28). Blood samples for glucose determination were taken from fasted, non-anesthetized animals. The blood was obtained from the distal vessels of the tail. The blood for the other tests was withdrawn from animals under deep diethyl ether anesthesia by heart puncture at the time of necropsy.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
ORGAN WEIGHTS: Yes
The following exsanguinated organs of the animals sacrificed at necropsy were weighed in the unfixed state: adrenal glands, brain, epididymides, heart, kidneys, liver, spleen, testes, thymus. The organ weights are specified in both absolute and relative terms. The relative organ weights were calculated by normalization to 100 g body weight (individual organ weight divided by body weight times 100). The body weight used as a basis for this calculation was determined immediately prior to necropsy of the pertinent animal.
HISTOPATHOLOGY: Yes - Statistics:
- The quantitative results for individual animals were used to calculate arithmetic group means and standard deviations. The results for the groups that received the test substance were compared with those for the control group and significant differences indicated by "+" for p<0.05 and "++" for p<0.01. In case of numbers of values too low to calculate test statistics this is indicated by "nc".
The Dunnett test was used for body weight, body weight gain, feed consumption and organ weight data (relative organ weights subsequent to logarithmic transformation).. - Clinical signs:
- no effects observed
- Description (incidence and severity):
- No systemic clinical signs were observed
- Dermal irritation:
- no effects observed
- Description (incidence and severity):
- Skin reddening was not observed either in the control or in the dose group. During the entire treatment period, the mean skinfold thickness of the 1000 mg/kg group animals was comparable to the controls.
- Mortality:
- no mortality observed
- Description (incidence):
- No animal died throughout the entire treatment period.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- In males and in females, the body weights and the body weight development were not impaired. Through the entire study, in females at 1000 mg/kg bw/d, the body weights were slightly higher than in the controls.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- In male and in female animals, the food consumption per animal was unaffected by treatment. In males, at day 7 a very slight decrease of the daily feed intake per kg body weight was calculated. This statistically significant effect is regarded as incidental.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- There were no effects of treatment observed, neither on red blood cells, nor on leucocyte counts, on hemogram, or on blood coagulation. The statistically significantly decreased hemoglobin and hematocrit values in males are considered incidental. These effects were observed only in one sex, no individual values in the dose group are below the lower limit of the biological range for animals of this age. Additionally, the control values are very high, they exceed the 2s range.
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- There were no toxicologically significant changes in clinical chemical parameters. The observed statistically significant differences of the activity of alanine aminotransferase and of the concentration of triglycerides and creatinine in males, as well as of the concentration of inorganic phosphate in females are considered incidental. These effects were observed only in one sex, and all individual values are in the biological range for animals of this age.
- Endocrine findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- No significant differences to the controls were observed.
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- There were no local or systemic histopathological findings attributable to the test substance in the organs/tissues examined.
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
- Description (incidence and severity):
- Skin reactions
- Details on results:
- Regarding survival rate, state of health, or general behavior of the animals there was no difference between the treated and untreated animals. At 1000 mg/kg no macro- or microscopical skin findings were observed. At 1000 mg/kg the feed consumption and the body weights did not differ
lexicologically significantly from those in the controls. Hematology tests afforded no evidence for a treatment-related effect at 1000 mg/kg. Neither the hematopoetic system nor the red and white blood cell populations or blood coagulation were affected. The results of clinical laboratory tests, gross pathology, organ gravimetry and histopathology afforded no evidence for a treatment-related effect. - Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Systemic toxicity
- Effect level:
- 1 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Local effects
- Effect level:
- 1 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- A 28-day dermal toxicity study in the rat was performed at the limit dose of 1000 mg/kg bw/d. A NOAEL of1000 mg/kg bw/d is reported for local and systemic effects.
- Executive summary:
In this sub-acute repeated dose toxicity study, groups of 5 male and 5 female Wistar rats were administered spirodiclofen at dose levels of 0 (controls) and 1000 mg/kg bw/d by dermal application. Analytical determinations of stability and homogeneity were not performed because the test substance was applied undiluted and only moistened with water immediately before application. Males and females received 22 applications within a total period of 28 days. The exposure time per day was 6 hours. General observations: No effects on body weight development, food consumption, clinical signs, or skin reactions were seen. Clinical chemistry and hematology did not reveal any treatment-related changes. The results of gross pathology, organ weight analysis and histopathology did not reveal evidence of a treatment-related effect. In conclusion, neither systemic nor local skin effects were observed after a dermal administration of 1000 mg/kg bw/d to rats for four weeks. 1000 mg/kg bt/d is therefore regarded as the NOAEL for local and systemic effects in male and female rats.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- 1 000
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- A GLP- and guideline compliant 28-day dermal toxicity study in the rat (Klimisch =1) is available
Additional information
Justification for classification or non-classification
Spirodiclofen has a harmonised classification for STOT RE 2 on the basis of the available data. The relevant part of the RAC Conclusion is summarised below:
Mouse studies
RAC concluded that in the oral repeated dose toxicity studies in the mouse (13-week & 18-month) there was no evidence for severe liver effects such as organ lesions or dysfunction. Classification for STOT RE based on the mouse studies was not justified.
Rat studies
The effect levels in the 4-week, 14-week and 2-year rat repeated dose toxicity studies were mostly above the upper limit for STOT RE classification. Increased small cortical vacuolisation of the adrenals (with increased severity grading) was observed in males at dose levels of 6.6 and 32.1 mg/kg bw/d and higher in the 14-week study (below the guidance valuefor STOT RE 2 classification). However this was within the range of historical controls. Additionally, the results from the combined chronic toxicity/carcinogenicity, 2-generation reproductive toxicity, neurotoxicity and immunotoxicity studies did not warrant classification for STOT RE.
Dog studies
In the available repeated dose toxicity studies in dogs (4-week, 8-week, 14-weekand 1-year) many parameters of various organ systems were affected including the haematological system, the liver and the adrenals. The observed adrenal effects in dogs (cytoplasmic vacuolisation and mononuclear cell infiltration adrenal cortex effects) were considered not to be severe and not to fulfil the CLP criteria for STOT RE classification. Effects on the haematological system were not observed in the 8-week and 1-year dog studies. However, they were seen in the 4-week and 14-week dog studies. In both studies the effect levels were below the upper limit for STOT RE 2. In the 4-week study reduced erythrocytes, Hb and Hct were observed. In the 14-week study though, a dose related effect on Hb and Hct evels and erythrocyte count was seen and at the highest dose level a 20% decline of these parameters was observed which is considered a consistent and adverse effect. The liver was also identified as a target organ in dogs. Effects included increased organ weight and increased biochemical parameters. Also hepatocellular necrosis was observed although at effect-levels below the upper limit for STOT RE 2 classification.
STOT RE 2 classification is therefore based on haematology and liver effects and apply to all routes of exposure.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.