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EC number: 240-886-8 | CAS number: 16867-03-1
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 06.10.2003 - 03.05.2004
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.2600 (Skin Sensitisation)
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 2-aminopyridin-3-ol
- EC Number:
- 240-886-8
- EC Name:
- 2-aminopyridin-3-ol
- Cas Number:
- 16867-03-1
- Molecular formula:
- C5H6N2O
- IUPAC Name:
- 2-aminopyridin-3-ol
1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- Number of animals: 15 females (three groups of five females each group), nulliparous and non-pregnant.
Age and bodyweight: Young adult animals (approx. 11 weeks old} were selected. Body weight variation was within +/- 20% of the sex mean.
Identification: Tailmark.
Control animals: The vehicle control animals were treated using the same vehicle, using the same procedures and within the same time frame as this study.
Conditions:
Animals were housed in a controlled environment, in which optimal conditions were considered to be approximately 15 air changes per hour, a temperature of 21.0 ± 3.0°C (actual range: 19.3 - 21.4°C), a relative humidity of 30-70% (actual range: 33 - 72%) and 12 hours artificial fluorescent light and 12 hours darkness per day.
Cleaning procedures in the room might have caused the temporary fluctuations above the optimal maximum level of 70% for relative humidity. Based on laboratory historical data, these fluctuations were considered not to have affected the study integrity.
Accommodation:
Individual housing in labelled Macrolon cages (type I; height 12.5 cm) containing purified sawdust as bedding material (Woody-Clean type 3/4; Tecnilab-BMI BV, Someren, The Netherlands). Certificates of analysis were examined and then retained in the NOTOX archives. The acclimatisation period was at least 5 days before the start of treatment under laboratory conditions. Animals were group housed in polycarbonate cages (Macrolon II type; height 15 cm) during the acclimatisation period.
Diet:
Free access to standard pelleted laboratory animal diet (from Altromin (code VRF 1 ), Lage, Germany).
Water:
Free access to tap-water.
Study design: in vivo (LLNA)
- Vehicle:
- other: Ethanol : water (7:3 v/v)
- Concentration:
- 0% (vehicle control), 5%, 25%, 50%
- No. of animals per dose:
- 5
Results and discussion
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 2.9
- Test group / Remarks:
- group 1, 5%
- Parameter:
- SI
- Value:
- 1.7
- Test group / Remarks:
- group 2, 25%
- Parameter:
- SI
- Value:
- 1.9
- Test group / Remarks:
- group 3, 50%
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information
- Conclusions:
- The Sl values calculated for the substance concentrations 5, 25 and 50% were 2.9, 1.7 and 1.9 respectively.
There was no indication that the test substance could elicit an SI ≥3.
Based on these results and according to the recommendations made in the test guidelines (OECD No.429, EC 8.42 and EPA OPPTS 870.2600), A 132 should not be regarded as a skin sensitiser.
Based on these results and according to the:
- OECD Harmonized lntegrated Hazard Classification System for Human Health and Environmental Effects of Chemical Substances (OECD, 1998), A 132 does not have to be classified for sensitisation by skin contact.
- EC criteria for classification and labelling requirements for dangerous substances and preparations (Council Directive 67/548/EEC), A 132 does not have to be classified and has no obligatory labelling requirement for sensitisation by skin contact. - Executive summary:
Assessment for Contact Hypersensitivity to A 132 in the Mouse (Local Lymph Node Assay).
The study was carried out based on the guidelines described in: OECD, Section 4, Health Effects, No.429 (2002), Paris Cedex; EC, Council Directive 67/548/EEC, Annex IV C, B.42 (Draft) (2001 ); Environmental Protection Agency (EPA): Health Effects Test Guidelines OPPTS 870.2600. "Skin Sensitisation" 2003.
Test substance concentrations selected for the main study were based on the results of a preliminary study.
In the main study, three groups of five experimental animals were epidermally exposed to a 5%, 25% and 50% concentration respectively on three consecutive days. Five vehicle control animals were similarly treated, but with vehicle alone (Ethanol:water (7:3 v/v).
Three days after the last exposure, all animals were injected with 3H-methyl thymidine and after five hours the draining (auricular) lymph nodes were excised.
After precipitating the DNA of the lymph node cells, radioactivity measurements were done.
All the nodes were equal in size.
Mean DPM/animal values for the experimental groups treated with test substance concentrations 5, 25 and 50% were 332, 192 and 220 respectively. The mean DPM/animal value for the vehicle control group was 113.
The SI values calculated for the substance concentrations 5, 25 and 50% were 2.9, 1. 7 and 1.9 respectively.
There was no indication that the test substance could elicit an SI ≥3.
Based on these results and according to the recommendations made in the test guidelines (OECD No.429, EC B.42 and EPA OPPTS 870.2600), A 132 should not be regarded as a skin sensitiser.
Based on these results and according to the:
- OECD Harmonized lntegrated Hazard Classification System for Human Health and Environmental Effects of Chemical Substances (OECD, 1998), A 132 does not have to be classified for sensitisation by skin contact.
- EC criteria for classification and labelling requirements for dangerous substances and preparations (Council Directive 67/548/EEC), A 132 does not have to be classified and has no obligatory labelling requirement for sensitisation by skin contact.
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.
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