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EC number: 268-717-3 | CAS number: 68133-90-4
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 Feb 2020 - 29 Jun 2020
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- An EPMF member company received an official request from the Korean authorities to perform the in vivo mutagenicity assay with hexahydroxyplatinate,compound with 2-aminoethanol(1:2) (CAS 68133-90-4), ahead of the formal testing proposal approval by ECHA. The requested experimental information is in line with the assay submitted in the TP for this substance. The deadline given by the Korean authorities was however much tighter than the anticipated date of receiving the final decision on the TP. Therefore, the in vivo mutagenicity testing with this substance has been initiated in the EU prior to receiving the final decision on the TP.
In the attached document (translation from Korean and anonymised), a justification for initiating the in vivo muta testing upon official request from an non-EU authority (i.e. request outside EU-REACH), ahead of receiving the final decision on the TP. More information is available upon request.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Reference
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 Feb 2020 - 29 Jun 2020
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- An EPMF member company received an official request from the Korean authorities to perform the in vivo mutagenicity assay with hexahydroxyplatinate,compound with 2-aminoethanol(1:2) (CAS 68133-90-4), ahead of the formal testing proposal approval by ECHA. The requested experimental information is in line with the assay submitted in the TP for this substance. The deadline given by the Korean authorities was however much tighter than the anticipated date of receiving the final decision on the TP. Therefore, the in vivo mutagenicity testing with this substance has been initiated in the EU prior to receiving the final decision on the TP.
In the attached document (translation from Korean and anonymised), a justification for initiating the in vivo muta testing upon official request from an non-EU authority (i.e. request outside EU-REACH), ahead of receiving the final decision on the TP. More information is available upon request. - Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 29 July 2016
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian erythrocyte micronucleus test
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Lot/batch number of test material:
19267COLPT.
- Expiration date of the lot/batch: 01 October 2021.
- Purity test date: CoA issued 17 December 2019.
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: At room temperature.
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: None.
- Final preparation of a solid: Test item was suspended in corn oil.
FORM AS APPLIED IN THE TEST (if different from that of starting material)
: Suspension. - Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- The Wistar Han rat was the species and strain of choice because it is a readily available rodent which is commonly used for genotoxicity testing, with documented susceptibility to a wide range of toxic items. Moreover, historical control background data has been generated with this strain.
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany.
- Age at study initiation: 6 weeks.
- Weight at study initiation: 171 ± 8.7 g (Mean body weight ± SD).
- Assigned to test groups randomly: Yes.
- Fasting period before study: No.
- Housing: Up to 5 animals of the same sex and in the same dosing group were housed together.
- Diet: Commercial pellets ad libitum, except during designated procedures.
- Water: Tap water, ad libitum.
- Acclimation period: At least 6 days.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 25°C.
- Humidity (%): 40 to 70%.
- Air changes (per hr): ≥ 10.
- Photoperiod: 12 hrs light/12 hrs dark, except during designated procedures.
IN-LIFE DATES:
From: Not specified.
To: 12 Mar 2020. - Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil.
- Source of vehicle: Fagron Farmaceuticals, Capelle a/d IJssel, the Netherlands. - Duration of treatment / exposure:
- Three consecutive days.
- Frequency of treatment:
- Daily.
- Post exposure period:
- Tissue samples taken 3 - 4 hours after administration of final dose.
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- Remarks:
- No treatment-related toxicity or mortality were in a preliminary dose range finding study in which three male and three female rats received three consecutive daily doses of 2000 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide.
- Route of administration: Gavage.
- Doses / concentrations: A single dose of 19 mg/kg bw, dissolved in physiological saline. - Tissues and cell types examined:
- Bone marrow from the femur.
- Details of tissue and slide preparation:
- The femurs were flushed with foetal calf serum and the cell suspension centrifuged. The supernatant was removed and a drop of the remaining cell suspension was spread across a clean slide and fixed with methanol. The slides were automatically stained with Giemsa using the Wright Stain Procedure.
- Evaluation criteria:
- The test item was considered positive if all of the following criteria were met:
a) at least one treatment group showed a statistically significant increase in frequency of micronucleated polychromatic erythrocytes.
b) the increase was dose related.
c) the results were outside the 95% confidence limits of the historical control data.
If none of the above criteria were met, and bone marrow exposure to the test item occurred, the substance was considered negative.
The incidence of micronuclei was assessed in 8000 polychromatic erythrocytes per animal. - Statistics:
- ToxRat Professional v 3.2.1 (ToxRat Solutions® GmbH, Germany) was used for statistical
analysis of the data.
A test item is considered positive in the micronucleus test if all of the following criteria are
met:
a) At least one of the treatment groups exhibits a statistically significant (one-sided,
p < 0.05) increase in the frequency of micronucleated polychromatic erythrocytes
compared with the concurrent negative control
b) The increase is dose related when evaluated with a trend test.
c) Any of the results are outside the 95% control limits of the historical control data range.
A test item is considered negative in the micronucleus test if:
a) None of the treatment groups exhibits a statistically significant (one-sided, p < 0.05)
increase in the frequency of micronucleated polychromatic erythrocytes compared with
the concurrent negative control.
b) There is no concentration-related increase when evaluated with a trend test.
c) All results are within the 95% control limits of the negative historical control data range.
As there were statistically significant differences between one or more of the test item groups
and the vehicle control group a Cochran Armitage trend test (p < 0.05) was performed to test
whether there is a significant trend in the induction. - Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Platinum was quantifiable in plasma samples from high-dose (2000 mg/kg bw/day) satellite animals 1, 3, 6 and 12 hours after completing the second day of treatment. Moreover, platinum was quantifiable in plasma samples from all high-dose animals taken at necropsy approximately 3-4 hours after the third dose. Therefore it was confirmed that the bone marrow was exposed to the test item. No test item was detected in the animals dosed with vehicle.
No statistically significant increase in the frequency of micronucleated polychromatic erythrocytes was observed.
Treated animals showed no decrease in the PCE:NCE ratio, indicating a lack of toxicity to the bone marrow. - Conclusions:
- Dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol, did not induce an increase in micronucleated polychromatic erythrocytes in rats administered up to 2000 mg/kg bw/day by gavage on three consecutive days.
- Executive summary:
The in vivo clastogenicity and aneugenicity of dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol, as evaluated by its ability to induce micronuclei in polychromatic erythrocytes, was assessed in a study following OECD 474 and according to GLP. Male Wistar rats (5/group) were given gavage doses of 500, 1000 or 2000 mg/kg bw/day of the test item on three consecutive days, or a vehicle control. The concurrent positive control group received a single dose of cyclophosphamide. Bone marrow was harvested from the femurs and assessed for micronuclei.
There was no increase in the number of micronucleated polychromatic erythrocytes in any treatment group. On that basis, dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol, was concluded to be non-genotoxic under the conditions of this assay.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 020
- Report date:
- 2020
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 489 (In vivo Mammalian Alkaline Comet Assay)
- Version / remarks:
- 29 July 2016.
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian comet assay
Test material
- Reference substance name:
- Dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol (1:2)
- EC Number:
- 268-717-3
- EC Name:
- Dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol (1:2)
- Cas Number:
- 68133-90-4
- Molecular formula:
- C2H7NO.1/2H6O6Pt.H
- IUPAC Name:
- dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol (1:2)
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Lot/batch number of test material:
19267COLPT.
- Expiration date of the lot/batch: 01 October 2021.
- Purity test date: CoA issued 17 December 2019.
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: At room temperature.
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: None.
- Final preparation of a solid: Test item was suspended in corn oil.
FORM AS APPLIED IN THE TEST (if different from that of starting material)
: Suspension.
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- The Wistar Han rat was the species and strain of choice because it is a readily available rodent which is commonly used for genotoxicity testing, with documented susceptibility to a wide range of toxic items. Moreover, historical control background data has been generated with this strain.
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany.
- Age at study initiation: 6 weeks.
- Weight at study initiation: 171 ± 8.7 g (Mean body weight ± SD).
- Assigned to test groups randomly: Yes.
- Fasting period before study: No.
- Housing: Up to 5 animals of the same sex and in the same dosing group were housed together.
- Diet: Commercial pellets ad libitum, except during designated procedures.
- Water: Tap water, ad libitum.
- Acclimation period: At least 6 days.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 25°C.
- Humidity (%): 40 to 70%.
- Air changes (per hr): ≥ 10.
- Photoperiod: 12 hrs light/12 hrs dark, except during designated procedures.
IN-LIFE DATES:
From: Not specified.
To: 12 Mar 2020.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil.
- Source of vehicle: Fagron Farmaceuticals, Capelle a/d IJssel, the Netherlands. - Duration of treatment / exposure:
- Three consecutive days.
- Frequency of treatment:
- Daily.
- Post exposure period:
- Tissue samples taken 3 - 4 hours after administration of final dose.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- Remarks:
- No treatment-related toxicity or mortality were seen in a preliminary dose range finding study in which three male and three female rats received three consecutive daily doses of 2000 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Ethyl methanesulphonate.
- Route of administration: Gavage.
- Doses / concentrations: 200 mg/kg bw, dissolved in physiological saline, administered twice.
Examinations
- Tissues and cell types examined:
- Cells were isolated from the liver, glandular stomach, duodenum and kidney.
- Details of tissue and slide preparation:
- Minced liver or kidney tissue was added to collagenase and dissolved in HBSS (saline). This suspension was shaken and centrifuged. The cell pellet was resuspended in HBSS and kept on ice prior to preparation of the slides.
Tissue from the glandular stomach and duodenum was stored on ice in "mincing buffer incomplete" (HBSS + EDTA). The surface epithelium of both the glandular stomach and duodenum was discarded as it contains a high proportion of apoptotic cells which distort the comet analysis. The cells, suspended in the buffer, were filtered though a 100 µm cell strainer and stored on ice prior to preparation of the slides.
Low melting point agarose was added to the cell suspensions and layered on a comet slide, which was then incubated for 13 - 39 minutes in the refrigerator.
Slides were kept overnight in the refrigerator, immersed in pre-chilled lysis solution. After rinsing, the slides were placed in freshly-prepared alkaline solution; electrophoresis was performed for 20 minutes (stomach and duodenum) or 30 minutes (liver and kidney). Following another rinse, the slides were immersed in absolute ethanol and allowed to dry, before staining with SYBR Gold fluorescent dye. - Evaluation criteria:
- A test item was considered positive if all of the following criteria were met:
a) at least one treatment group demonstrated a statistically significant increase in % tail intensity vs. control.
b) the increase was dose-related.
c) any of the results were outside the 95% confidence limits of the historical control data.
If none of the above criteria were met, and direct or indirect evidence supportive of exposure of, or toxicity to, the target tissues was demonstrated, the test item was considered negative. If the data precluded making a conclusion of clearly positive or negative, the result was concluded as equivocal. - Statistics:
- ToxRat Professional v 3.2.1 (ToxRat Solutions® GmbH, Germany) was used for statistical
analysis of the comet assay data .
A test item is considered positive in the Comet assay if all of the following criteria are met:
a) At least one of the treatment groups exhibits a statistically significant (one-sided, p <
0.05) increase in percentage Tail Intensity is detected compared with the concurrent
negative control.
b) The increase is dose related when evaluated with a trend test.
c) Any of the results are outside the 95% control limits of the historical control data range.
A test item is considered negative in the Comet assay if:
a) None of the treatment groups exhibits a statistically significant (one-sided, p < 0.05)
increase in percentage Tail Intensity is detected compared with the concurrent negative
control.
b) There is no concentration-related increase when evaluated with a trend test.
c) All results are within the 95% control limits of the negative historical control data range.
Results and discussion
Test resultsopen allclose all
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- Kidney: no statistically significant increase in % tail intensity.
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- Liver: no statistically significant increase in % tail intensity.
- Toxicity:
- not examined
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- Glandular stomach: no statistically significant increase in % tail intensity.
- Toxicity:
- not examined
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- Duodenum: no statistically significant increase in % tail intensity.
- Toxicity:
- not examined
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
Platinum was quantifiable in plasma samples from high-dose (2000 mg/kg bw/day) satellite animals 1, 3, 6 and 12 hours after completing the second day of treatment. Moreover, platinum was quantifiable in plasma samples from all high-dose animals taken at necropsy approximately 3-4 hours after the third dose. Therefore it was confirmed that the target tissues were exposed to the test item. No test item was detected in the animals dosed with vehicle.
Any other information on results incl. tables
Historical data Comet assay Negative control
|
Liver Males and Females |
Duodenum Males and Females |
Stomach Males and Females |
Kidney Males and Females |
Mean |
1.96 |
3.06 |
2.45 |
12.10 |
SD |
0.92 |
1.52 |
1.39 |
8.46 |
n |
85 |
45 |
60 |
30 |
Lower control limit (95% control limits) |
0.27 |
-0.86 |
-1.07 |
-1.35 |
Upper control limit (95% control limits) |
3.65 |
6.97 |
5.96 |
25.55 |
SD = Standard deviation
n = Number of observations
Kidney: Historical control data from experiments performed in Feb 2012 – July 2019
Liver, Stomach, Duodenum: Historical control data from experiments performed in Jan 2018 – July 2019
Applicant's summary and conclusion
- Conclusions:
- When tested in the comet assay, dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol, did not induce an increase in DNA damage in the liver, kidney, glandular stomach or duodenum of rats administered up to 2000 mg/kg bw/day by gavage on three consecutive days. As such, this compound was considered to negative under the conditions of this assay.
- Executive summary:
The potential for dihydrogen hexahydroxyplatinate, compound with 2-aminoethanol, to cause DNA damage was evaluated in a study following OECD 489 and according to GLP. Male Wistar rats (5/group) were given gavage doses of 500, 1000 or 2000 mg/kg bw/day of the test item on three consecutive days, or a vehicle control. The concurrent positive control group received two doses of EMS (200 mg/kg bw/day). Comet analyses were conducted on preparations of liver, glandular stomach, duodenum and kidney tissues.
There was no increase in % tail intensity in the liver, kidney, glandular stomach or duodenum, indicating that the test item is not genotoxic to these tissues.
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