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EC number: 284-892-9 | CAS number: 84989-04-8 The fraction of tar acid rich in 3- and 4-methylphenol, recovered by distillation of low-temperature coal tar crude tar acids.
- 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 water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
All cresol isomers (o-, m- and p-cresol) are readily biodegradable
o-, m-, and p-cresol: BOD 80% - 95% (OECD 301 C)
o-cresol: BOD = 86% (OECD 301 D)
m-cresol: BOD = 90% (OECD 301 D)
Key value for chemical safety assessment
Additional information
studies on ready biodegradability
Desai et al. (1990) determined the kinetics of o-, m- and p-cresol using an electrolytic respirometer test comparable to OECD guideline 301 C. Activated sludge from a wastewater treatment plant receiving predominantly domestic sewage was used as inoculum in a concentration of 30 mg/L. Within an incubation period of 40 days degradation of cresol isomers (initial concentration 100 mg/L) was in the range of 80% to 95%. The specific oxygen uptake curves of the cresols are not reported. However, the authors state that all test compounds revealed the same pattern: the lag phase, biodegradation phase and the plateau phase within a period of 10 days. Therefore, it can be concluded from this test that o-, m- and p-cresol are readily biodegradable.
The test system and test conditions used by Buzzel (1968) are similar to those described in the OECD guideline 301 D, e.g. a high substance/inoculum ratio and the use of a non-adapted inoculum. The specific oxygen uptake curves are reported. After a short lag phase a plateau is reached within 10 days. After 20 days 86% of o-cresol has been degraded. A half-life time of 2 to 3 days is reported.
Biodegradation of m-cresol was tested in aquatic phase according to OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test). Degradation was 90% after 28 d and the 10 d window was fulfilled. Thus m-cresol is judged to be readily biodegradable (Bayer, 1988).
studies on inherent biodegradability
All cresol isomers are inherently degradable as shown by tests according to the OECD guideline 302 B. After a lag-period of 2 days 96% of the added m-cresol and 100% of the added p-cresol were degraded within 10 days, and a degradation of 100% within 7 days was observed for o-cresol (Wellens, 1990). The inherent biodegradability was also studied by Pitter (1976) in a test similar to OECD guideline 302 B. Using an adapted activated sludge, o-cresol degraded to 95% and m- and p-cresol to 96% each within 5 days.
anaerobic test systems
The most extensive study on o-cresol was conducted by(1981). Primary anaerobic sludges from 12 treatment plants receiving mainly domestic wastewater were diluted to 10% in a mineral salt medium and incubated with 30 mg o-cresol/L for 8 weeks. Degradation was followed by CH4and CO2evolution. For o-cresol, no anaerobic degradation was observed in any sludge.
In contrast to these findings p-cresol and m-cresol are biodegradable under anaerobic conditions. As measured from methane release and carbon dioxide formation m- and p-cresol are mineralized by anaerobic sludges from wastewater treatment plants (Shelton and Tietje 1981, 1984; Battersby and Wilson 1988, 1989).
marine test system
Biodegradation of p-cresol was also tested in seawater where it was biodegradable as well (Boyd and Carlucci 1993).
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