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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 201-964-7 | CAS number: 90-05-1
- 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
Biodegradation in soil
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in soil: simulation testing
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the substance is readily biodegradable
- Endpoint:
- biodegradation in soil, other
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: It was a study of primary degradation. This study was not a standardized method and no information was available about the test substance.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The rate of degradation of substituted benzenes by soil microorganisms was determined by a spectrophotometric technique (loss of UV absorbancy).
- GLP compliance:
- no
- Test type:
- other: primary degradation assay
- Radiolabelling:
- no
- Oxygen conditions:
- aerobic
- Soil classification:
- not specified
- Details on soil characteristics:
- Soil microorganisms used were from suspension of Niagara silt loam. No more data on the soil characteristics
- Duration:
- 64 d
- Initial conc.:
- 15 other: mg/l
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- test mat. analysis
- Temp.:
- 25°C
- Humidity:
- aqueous suspension of soil
- Microbial biomass:
- no data
- Details on experimental conditions:
- The solution contained the test compound as the sole carbon source to support microbial proliferation and 1.6 g K2HPO4, 0.4 g of KH2PO4, 0.5 g of NH4NO3, 0.2 g of MgSO4,7H2O, 25 mg of CaCl2,2H2O, 2.3 mg of FeCl3,6H2O and 1000 ml of distilled water. 40 ml aliquots of the medium were placed in 4-oz. screww cap bottles, 45 mm diameter x 80 mm high and these were inoculated with 1 ml of a 1% suspension of Niagara silt loam. A parallel series of reaction vessels was set up identical to the first except that each bottle also contained 8 mg of HgCl2 and 5.10exp-7 M Tween 80. readings were made on these flasks at the same time intervals. Aniother series identical to the first was set up to determine if the chemical at the concentrations employed were toxic to the microflora; these vessels received glucose to a finalconc. of 1% and growth in the tube was recorded visually. The bottles were incubated in the dark at 25°C. At intervals of 3h, 6h, 1, 2, 4, 8, 16, 32 and 64 days after inoculation, the solutions were mixed, an aliquot was removed and the suspension was centrifuged.
- % Degr.:
- 100
- Parameter:
- test mat. analysis
- Sampling time:
- 4 d
- Conclusions:
- Guaiacol was found to be 100% biodegraded by a mixed soil microflora within 4 days, based on loss of UV absorbancy.
Referenceopen allclose all
Description of key information
Key value for chemical safety assessment
Additional information
According to column 2 of REACH Annex IX, study does not need to be conducted since Guaiacol is readily biodegradable. However, a study quoted as Klimisch 3 (Alexander & Lustigman, 1966) indicated biodegradation of substituted benzenes by soil microflora. Based on loss of UV absorbancy, the authors found that guaiacol was degraded by soil microorganisms in 4 days.
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.