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EC number: 231-210-2 | CAS number: 7447-39-4
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Already evaluated by the Competent Authorities for Biocides and Existing Substance Regulations.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3700 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: MAFF guideline 59 NohSan Np. 4200 (1985)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.31 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- GLP compliance:
- yes
- Remarks:
- Self-certified laboratory
- Limit test:
- no
Test material
- Reference substance name:
- Copper hydroxide
- EC Number:
- 215-705-0
- EC Name:
- Copper hydroxide
- Cas Number:
- 1344-69-0
- IUPAC Name:
- copper(1+) hydroxide
- Details on test material:
- Test material: Copper hydroxide
Lot/Batch number: 021121/1
Purity: 61.14 % copper
Description: Free flowing blue product, needles.
Stability: No evidence of instability was observed.
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- Source: Covance, Denver, Pennsylvania, USA.
Sex: Female.
Age at study initiation: approximately 5 months.
Weight at study initiation: 2988 to 4412 g (on day 0 of gestation).
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: 0.5 % aqueous methylcellulose
- Details on exposure:
- Concentration in vehicle: 0, 6, 9, or 18 mg Cu/mL
Total volume applied: 1mL/kg bw - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis of dose formulations confirmed stability, homogeneity and verified the accuracy of formulation.
- Details on mating procedure:
- Mating period: Not specified.
- Duration of treatment / exposure:
- Duration of exposure: Day 7–28 of gestation.
- No. of animals per sex per dose:
- Number of animals per group: 22 females (1 rabbit of the high dose group was removed on day 7 of gestation, prior to dosing, due to a self-inflicted injury).
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- Body weight: Yes (daily)
Food consumption: Yes (daily)
Clinical signs: Yes (daily)
Gross pathology and histopathology: Yes, gross external and visceral examination was performed for all animals.
Post-exposure period: Sacrifice on day 29 of gestation. - Ovaries and uterine content:
- Examination of uterine content: Gravid uterine weight, number of corpora lutea, number of implantations, number of resorptions.
- Fetal examinations:
- General: Litter Size, number of live and dead foetuses, foetal weight, sex ratio, external alterations, retarded renal development.
Skeleton: Yes
Soft tissue: Yes - Statistics:
- Linear contrast of means (Maternal weight, weight change, food consumption);
Jonckheere’s test (Live and dead foetuses, resorptions, implantations, incidence of foetal alterations);
Cochran-Armitage test (Incidence of pregnancy, clinical observations, maternal mortality, females with total resorptions, abortions/early deliveries);
Linear contrast of least square means (foetal weight, sex ratio).
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Three females of the high dose group were found dead during the study. One of them showed diarrhoea, red cageboard-staining, weakness, and irregular respiration prior to death. Gross necropsy of the three animals included stomach haemorrhage and/or ulceration, dark discolouration or mottling of lung tissue, pale liver, gelatinous tan rectal discharge, and brown liquid in chest cavity. In addition, two females of this dose group aborted. Diarrhoea was observed for one of them and the other animal showed red discoloured stomach lining upon necropsy. No mortality occurred at the low and mid dose levels. All animals of the test substance groups showed diarrhoea. Statistically significant adverse effects on maternal body weights, body weight changes and food consumption were observed at 9 and 18 mg Cu/kg bw/day. Marked reduction in food consumption and body weight losses were observed during the 1st week of dosing. The results are presented in Table 1.
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- 6 mg/kg bw/day
- Based on:
- element
- Basis for effect level:
- other: Maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
The number of foetuses, and numbers of early and late embryonic deaths were not adversely affected by maternal treatment. Mean foetal weight was slightly lower at 18 mg/kg bw/day (9 % lower than controls). The difference from control was considered treatment-related, but it was not statistically significant. The results are presented in Table 2.
There was a total of four foetuses with malformations: one control foetus showed fused ribs, one foetus at 6 mg/kg bw/day showed ectopic kidney, and two foetuses (from separate litters) at 18 mg/kg bw/day showed hemivertebra. These malformations were considered spontaneous and unrelated to treatment. There was a slight increase in incidence of foetuses at 18 mg/kg bw/day with retarded ossification of skull and pelvic bones. However, there was no correlation with foetal weight, and the biological significance of such a slight increase is uncertain, as there was no increase in the incidence of retarded sternebral ossification. Retarded sternebral ossification is a more common indicator of foetal immaturity. Rib alterations occurred at a very high incidence across all groups in this study; almost all litters were affected. The biological significance of an increase in incidence of a very common finding is uncertain. The results are presented in Table 3.
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- 6 mg/kg bw/day
- Based on:
- element
- Basis for effect level:
- other: Developmental toxicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Table 1. Maternal effects.
Parameter |
Control |
low dose |
mid dose |
high dose |
dose response |
Number of dams examined |
22 |
22 |
22 |
21 |
|
Clinical findings during application of test substance Alopecia |
2 |
5 |
2 |
1 |
- |
Mortality of dams (%) |
0 |
0 |
0 |
14 %* |
- |
Abortions |
0 |
1 |
0 |
2 |
- |
Body weight gain (day 7-29 of gestation) [g] |
261.5±130.42 |
208.5±158.50 |
179.5±160.97 |
72.6±211.64* |
+ |
Food consumption (day 7-29 of gestation) [g/day] |
144.1 ± 10.61 |
134.8 ± 21.36 |
120.3 ± 32.62* |
100.6±32.02* |
+ |
Pregnancies |
21 |
21 |
21 |
21 |
- |
* statistically significant trend ( p < 0.05) |
Table 2. Litter response (Caesarean section data).
Parameter |
Control |
low dose |
medium dose |
high dose |
dose response + / - |
No. mated |
22 |
22 |
22 |
21 |
|
No. pregnant |
21 |
21 |
21 |
21 |
- |
No. aborted/delivered early |
0 |
1 |
0 |
2 |
- |
No. found dead |
0 |
0 |
0 |
3* |
- |
No. accidentally killed |
0 |
0 |
0 |
1 |
- |
No. with total resorptions |
0 |
1 |
0 |
0 |
- |
Total number of litters |
21 |
19 |
21 |
15 |
- |
Means per litter: |
|
|
|
|
|
Mean corpora lutea |
10.0±2.06 |
10.2±1.51 |
9.1±1.96 |
10.1±2.26 |
- |
Implantation/Nidations |
8.8±2.04 |
9.0±1.33 |
7.8±2.04 |
9.0±2.36 |
- |
Resorptions Total |
1.0±1.47 |
1.0±1.45 |
0.2±0.54 |
0.6±0.91 |
- |
No. of dead fetuses |
0 |
0 |
0 |
0 |
- |
No. of Live fetuses Total |
7.9±2.63 |
8.0±1.73 |
7.6±2.04 |
8.4±2.03 |
- |
Mean fetal weight Total |
42.95±2.98 |
41.71±4.51 |
43.93±5.88 |
38.91±4.82 |
- |
Fetal sex ratio |
0.48±0.16 |
0.58±0.18 |
0.50±0.22 |
0.48 ±0.23 |
- |
* significant trend (p£ 0.05) |
Table 3. Examination of the fetuses.
Parameter |
Control |
low dose |
medium dose |
high dose |
dose response |
No. examined (no. of litters) |
165 (21) |
152 (19) |
159 (21) |
126 (15) |
|
No. of fetuses (litters) with: |
|
|
|
|
|
External malformations |
0 |
0 |
0 |
0 |
- |
External developmental variations |
0 |
0 |
0 |
0 |
- |
External variations due to retarded development |
0 |
0 |
0 |
0 |
- |
Skeletal malformations Rib- fused |
1 (1) |
0 |
0 |
0 |
- |
Skeletal developmental variations Rib- supernumerary |
105 (21) |
102 (19) |
127 (20) |
110 (15)* |
- |
Skeletal variations due to retarded development Mandible- retarded ossification |
0 |
0 |
0 |
1 (1) |
- |
Visceral malformations Kidney- ectopic |
0 |
1 (1) |
0 |
0 |
- |
Visceral developmental variations |
0 |
0 |
0 |
0 |
- |
Visceral variations due to retarded development Kidney: Small papilla- size 2 |
|
|
|
|
|
Total (%) with retardation |
68 (41%) |
67 (44%) |
80 (50%) |
57 (45%) |
- |
Total (%) with variations |
125 (76%) |
124 (82%) |
143 (90%) |
118 (94%) |
- |
* statistically significant trend (p < 0.05) |
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the current study, there was no evidence of test substance-related teratogenicity.
LO(A)EL maternal toxic effects: 9 mg Cu/kg bw/day
NO(A)EL maternal toxic effects: 6 mg Cu/kg bw/day
LO(A)EL developmental effects: 9 mg Cu/kg bw/day
NO(A)EL developmental effects: 6 mg Cu/kg bw/day - Executive summary:
Materials and Methods
Copper hydroxide was administered at concentrations of 0, 6, 9, or 18 mg Cu/kg bw to pregnant rabbits by gavage from day 7 to day 28 of gestation. Potential effects on maternal and developmental parameters were assessed. The study was conducted according to OECD 414 (1981); method B.31 (87/302/EEC), and USEPA OPPTS 870.3700 (1998).
Results and Discussion
Administration of copper to pregnant rabbits at 18 mg/kg bw/day was associated with marked initial bodyweight loss, inappetance, abortion and death. Pups in litters from surviving dams showed slightly lower mean foetal weight, and slightly increased incidence of a common skeletal variant. Maternal treatment at 9 mg/kg bw/day was associated with initial bodyweight loss and inappetance; pups also showed slightly increased incidence of a common skeletal variant, but mean foetal weights were not adversely affected. Maternal administration of copper hydroxide was not associated with increased incidence of foetal malformations, pre-implantation losses, or foetal (embryonic) deaths. The maternal and foetal no observed effect level was 6 mg/kg bw/day, based on maternal weight loss, inappetance, and an increased incidence of a common skeletal variant in foetuses at 9 mg/kg bw/day.
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