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EC number: 276-696-7 | CAS number: 72490-01-8
- 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
Repeated dose toxicity: dermal
Administrative data
- Endpoint:
- short-term repeated dose toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 05 Mar 1985 to 27 Mar 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 410 (Repeated Dose Dermal Toxicity: 21/28-Day Study)
- Version / remarks:
- 1981
- Deviations:
- yes
- Remarks:
- An occlusive application was used and no statistical analyses were performed.
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Ethyl [2-(4-phenoxyphenoxy)ethyl]carbamate
- EC Number:
- 276-696-7
- EC Name:
- Ethyl [2-(4-phenoxyphenoxy)ethyl]carbamate
- Cas Number:
- 72490-01-8
- Molecular formula:
- C17 H19 N O4
- IUPAC Name:
- ethyl [2-(4-phenoxyphenoxy)ethyl]carbamate
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Crl:CD(SD)BR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Weight at study initiation: 241 – 362 g
- Housing: exclusive rooms, single housed in suspended stainless steel mesh cages
- Diet: Rat and mouse Maintenance diet, ad libitum
- Water: filtered main water, ad libitum via water bottles
- Acclimation period: about 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 - 25
- Humidity (%): 40 - 70
- Air changes (per hr): minimum 12
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 05 Mar 1985 To: 27 Mar 1985
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- corn oil
- Details on exposure:
- TEST SITE
- Area of exposure: non-abraded areas of skin
- % coverage: not less than 10 % - Duration of treatment / exposure:
- 21 days, 6 hours per day
- Frequency of treatment:
- Daily
Doses / concentrationsopen allclose all
- Dose / conc.:
- 20 mg/kg bw/day (actual dose received)
- Remarks:
- Group 2. Low dose
- Dose / conc.:
- 200 mg/kg bw/day (actual dose received)
- Remarks:
- Group 3. Mid dose
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- Remarks:
- Group 4. High dose
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Rationale for animal assignment: Random
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS:
- Time schedule: Daily
- Cage side observations: Viability/mortality (twice daily), detailed behavioural observation (once weekly),
DETAILED CLINICAL OBSERVATIONS:
- Time schedule: Daily, including skin irritation which was assessed according to the scale antioned in Any other information on material and method inlc tables.
BODY WEIGHT: Yes
- Time schedule for examinations: Weekly
FOOD CONSUMPTION: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/animal/day: Yes
OPHTHALMOSCOPIC EXAMINATION:
- Time schedule for examinations: No
HAEMATOLOGY:
- Time schedule for collection of blood: During the final week
- Anaesthetic used for blood collection: No
- Animals fasted: Yes (18 hours)
- How many animals: All animals
- Parameters: haemoglobin concentration(Hb), mean cell volume (MCV), red blood cell count (RBC) and indices: mean cell haemoglobin (MCH), packed cell volume (PCV), mean cell (haemoglobin concentration MCHC); total and differential white cell count (WBC) , platelet count.
CLINICAL CHEMISTRY:
- Time schedule for collection of blood: During the final week
- Animals fasted: Yes (18 hours)
- How many animals: All animals
- Parameters: glutamate oxaloacetate transaminase (GOT/AST), glutamate pyruvate transaminase (GPT/ALT), alkaline phosphatase (Alk.P), blood urea nitrogen (BUN), glucose, inorganic, bilirubin, creatinine, sodium, total protein (TP), potassium, albumin, calcium, albumin/globulin ratio.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (see Any other information on material and method inlc tables)
HISTOPATHOLOGY: Yes (see Any other information on material and method inlc tables)
Results and discussion
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- Local
- Effect level:
- > 2 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- other:
- Remarks:
- No effects observed
- Dose descriptor:
- NOAEL
- Remarks:
- Systemic
- Effect level:
- 200 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- organ weights and organ / body weight ratios
Target system / organ toxicity
- Critical effects observed:
- no
Any other information on results incl. tables
ANALYSIS OF FORMULATIONS
The results obtained during the first week of the study were slightly lower than expected (83 - 88 % of nominal). The samples were analysed again and the results obtained were considered to be satisfactory (90 – 94 %) of normal). The values obtained at week 3 were also considered to be acceptable (94 – 96 %).
MORTALITY
There were no deaths during the study.
CLINICAL OBSERVATIONS
There were no treatment-related clinical changes.
SKIN IRRITATION
There was no evidence skin irritation at the application site in any of the treated animals.
BODY WEIGHT
There were no treatment-related changes in body weight gain
FOOD CONSUMPTION
Mean food consumptions of test and control groups remained closely comparable and there were no treatment-related changes.
HAEMATOLOGY
There were no haematological changes associated with treatment.
CLINICAL CHEMISTRY
Clinical chemistry parameters were unaffected by treatment.
ORGAN WEIGHTS
A slight increase in absolute and relative liver weights of about 19 per cent was observed in the group 4 animals when compared with the respective control value. This change was considered to be treatment-related. There were no other
changes in absolute or relative organ weights associated with treatment.
MACROSCOPIC NECROPSY FINDINGS
All rats had fur loss on the abdominal skin, accompanied in some cases by sores. The severity was similar in all groups. These abdominal skin lesions were probably associated with the occlusion technique. The only finding in the internal viscera was occasional cases of hydronephrosis in the right kidney. There were no findings of any unusual nature or incidence to suggest any gross toxic effect.
MICROSCOPIC PATHOLOGY FINDINGS
Minor changes such as low grade hypergranulosis and acanthosis were present in samples of skin from the site of application of the corn oil vehicle in group 1 rats.
Histopathological changes in the treated skin site of group 4 rats were similar to those in group 1. There was no evidence of increased irritation associated the with application of the test article in corn oil.
The most common finding in the liver of both control and treated rats was minor foci of leucocyte accumulation. minimal hepatocellular hypertrophy was probably present in a few animals, as suggested by the slightly increased liver weights but this was difficult to define with certainty against the normal background variations based on the histopathology of relatively few animals. There was no evidence of any degenerative changes in either the liver or kidney to suggest any systemic toxicity due to test article application.
Table 1 Overview of results
Dose (mg/kg bw/day) |
0 |
0 |
20 |
20 |
200 |
200 |
2000 |
200 |
dr |
|
m |
f |
m |
f |
m |
f |
m |
f |
|
Mortality |
none |
|
|||||||
Clinical signs |
No treatment-related findings |
|
|||||||
Body Weight |
No treatment-related findings |
|
|||||||
Food consumption |
No treatment-related findings |
|
|||||||
Haematology |
No treatment-related findings |
|
|||||||
Clin. Chemistry |
|
|
|
|
|
|
|
|
|
ALAT |
|
|
|
|
|
d |
|
d |
|
ASAT |
|
|
|
|
|
d |
|
d |
|
Urinalysis |
Not performed |
|
|||||||
Organ weights |
|
|
|
|
|
|
|
|
|
liver |
|
|
|
|
dr |
|
ia,r |
ia,r |
|
gonads |
|
|
|
|
dr |
|
da,r |
|
|
kidneys |
|
|
|
|
|
|
da,r |
|
|
Pathology |
|
|
|
|
|
|
|
|
|
Macroscopy |
no treatment-related findings |
|
|||||||
Microscopy |
|
|
|
|
|
|
|
|
|
liver: hypertrophy |
0/5 |
0/5 |
0/5 |
0/5 |
0/5 |
0/5 |
2/5 |
3/5 |
|
kidney: hydronephrosis |
0/5 |
1/5 |
2/5 |
0/5 |
1/5 |
1/5 |
1/5 |
0/5 |
|
d/i decreased/increased, but not statistically significantly compared to the controls
a absolute organ weight
r relative organ weight
Applicant's summary and conclusion
- Conclusions:
- Based on increased liver weights and concomitant liver hypertrophy of half of the test animals, the systemic NOAEL is set at 200 mg/kg bw/day. Since no adverse local effects were observed, the local NOAEL is set at >2000 mg/kg bw/day.
- Executive summary:
An OECD TG 410-like study as performed in compliance with GLP to assess the subacute dermal toxicity. Groups of 5 male and 5 female Crl:CD(SD)BR rats were dermally exposed to 20, 200 and 2000 mg/kg test item under occlusive conditions for 21 days - 6 hours/day. An additional group was treated with the corn oil vehicle alone and acted as controls. Twice daily all animals were examined to detect any which were dead or moribund.All animals were examined once daily for clinical changes including skin irritation. Individual body weights were recorded on the first day of the test and at weekly intervals throughout the study. Individual food consumption was recorded at weekly intervals throughout the study. Individual blood samples were collected from the orbital sinus of all animals (after an 18 hours fast) during the final week of the study. Laboratory analysis (haematology and clinical chemistry) were performed on individual blood samples. The animals were killed by an intraperitoneal injection of pentobarbitone sodium solution and exsanguination, following about 19 hours without food. A full macroscopic examination was made.
No treatment-related local skin effects were observed. One control animal, four animals given 20 mg/kg and one animal given 200 mg/kg showed slight, mainly reversible erythema. No treatment-related effects were observed on mortality, clinical observations, body weight, food consumption and haematology. In clinical chemistry analyses, females given 200 and 2000 mg/kg showed decreased levels of ASAT (80 % and 82 % of control, respectively) and ALAT (65 and 60 % of control, respectively). These changes were not considered to be treatment-related, since decreases were observed and no dose-response relationship was noted. In both males and females of the 2000 mg/kg dose group, increased absolute liver weights (122 % of control) and relative liver weights (119 % of control) were noted. Male rats given 2000 mg/kg showed decreased absolute weights of the gonads (94 % of control) and kidneys (91 % of control). In male rats given 200 and 2000 mg/kg, decreased relative weights of the gonads (94 % and 92 % of control, respectively) and the kidneys (94 % and 89 % of control, respectively) were seen.
At necropsy, no treatment-related changes were observed. Histopathology showed mild renal hydronephrosis in the control group (1/10) and 20 mg/kg group (2/10). Mild to moderate renal hydronephrosis was seen in 2/10 rats of the 200 mg/kg dose group, and the symptom was severe in one animal of the highest dose group. Hypertrophy of the liver was observed in 5 rats of the highest dose group. In the absence of histopathological correlates at 200 mg/kg, the slight decreases in relative gonad and kidney weight at 200 mg/kg were not considered toxicologically relevant.
Based on increased liver weights and concomitant liver hypertrophy of half of the test animals, the systemic NOAEL is set at 200 mg/kg bw/day. Since no adverse local effects were observed, the local NOAEL is set at >2000 mg/kg bw/day.
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