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Diss Factsheets
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EC number: 203-397-0 | CAS number: 106-43-4
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Stability
Photodegradation in air:
The calculated atmospheric half-life of 4-chlorotoluene is 8.8 days (Bayer Industry Services, 2004).
Hydrolysis:
As chlorine is a ring substituent, hydrolysis is not expected to be an important process in determining the environmental fate of p-chlorotoluene (Jaber, 1984). Neutral pH values when dissolved in water and stability are basic properties of chlorotoluenes (Rossberg, 2000).
Biodegradation
Biodegradation in water: screening tests
Readily biodegradation:
After 14 d, 0 % of 4 -chlorotoluene were degraded preforming a ready biodegradabiltiy test corresponding to OECD 301C (MITI, 1992).
Inherently biodegradation:
4 -Chlorotoluene was degraded about 86 % after 28 d testing the inherent biodegradability of the test substance. Due to the significant elimination (68 %) within 3 h there is evidence that the disappearance of p-chlorotoluene is caused by physico-chemical effects rather than biodegradation processes.
Bioaccumulation
Bioaccumulation: aquatic/sediment
The bioconcentration factor for 4-chlorotoluene was determined at two different concentration levels using fish (MITI, 1992):
0.3 mg/L: BCF 21.9 - 76.5
0.03 mg/L: BCF 14 - 101.6
Transport and Distribution
Adsorption/desorption behaviour
The distribution behaviour of 4 -chlorotoluene between water and soil was determined according to OECD guideline 106 (batch method). Three different soils were used yielding the following results (RCC, 1992):
sand: Koc = 512.2
loamy sand: Koc = 327.1
sandy loam: Koc = 335.9
Henry's Law Constant
The Henrys Law Constant for 4 -chlorotoluene was calculated based on the Bond Method (446.8 Pa*m³/mole) as well as the Group Method (494.5 Pa*m³/mole) applying the EPI-Suite software (Bayer Industry Services, 2004).
Distribution Modelling
The distribution of p-chlorotoluene in a "unit world" was calculated according to the Mackay fugacity model level I (Bayer Industry Services, 2004) based on the physico-chemical properties of the test substance. The main target compartment for p-chlorotoluene is air with 99.67 %, followed by water with 0.24 %, and soil with 0.04%.
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