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EC number: 204-371-1 | CAS number: 120-12-7
- 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
Overview on measured bioaccumulation data in fish
The number of key publications that deserve reliability of 2 is limited: these include those of Japan CITI 1992/NITE 2002, Spacie et al. 1983, and to a certain degree those of de Voogt et al. 1991. The distribution of radiolabelled anthracene was investigated in one well-done lab-scale microcosm study that included several species and compartments (Lu et al 1978).
Reliable experimental BCF values based on valid studies with anthracene in fish range from about 1000 to about 2500.
This is largely consistent with the predicted BCF values obtained from the octanol-water partition coefficient.
Based on accepted calculations of the BCF (see EC TGD 2003, part 2, p. 126: lgBCF = 0.85*lgKow – 0.70, according to Veith et al. 1979) [also recommended in Guidance CSA (May 2008), Chapter R7C, Tab. R.7.10-3], the predicted BCF would be ~1900. Using the other published and commonly used lgKow of 4.54 (Karickhoff et al. 1979; WHO-EHC 202 1998), then a predicted BCF of 1440 results.
The Guidance CSA (May 2008), Chapter R7C, Tab. R.7.10-4 relates the logKow range from 4.5 to <5 with a BCF range in fish from 2000 to 5000. It is obvious that the BCF values of anthracene based on the logKow values are expected at the low end of this range, indicating B.
Species |
BCF |
Test system |
Type |
Val. |
References |
Fish |
|||||
Cyprinus carpio |
1660-2820 |
OECD 305 (15 µg/L) |
Equi (parent) |
2 |
CITI 1992 |
Cyprinus carpio |
903-2710 |
OECD 305 (1.5 µg/L) |
Equi (parent) |
2 |
CITI 1992 |
Gambusia affinis |
1029 |
lab-scale microcosm |
Equi (parent), |
2 |
Lu et al. 1978 |
L. macrochirus |
900 |
S |
k1/k2(total) |
2 |
Spacie et al. 1983 |
L. macrochirus |
675 |
S |
k1/k2(corrected) |
2? |
Spacie et al. 1983 |
P. reticulata |
3900 |
S |
Equi (parent) |
2 |
De Voogt et al. 1991a |
P. reticulata |
7260 |
S |
k1/k2(parent) |
3 |
De Voogt et al. 1991b |
P. reticulata |
4550 |
R |
Equi (parent) |
3 |
De Voogt et al. 1991c |
P. promelas |
6760 |
S |
k1/k2(parent) |
3 |
De Maagd et al., 1996 |
Carassius auratus |
162 |
S, initial conc. >> water solubility |
k1/k2(parent) |
3 |
Ogata et al. 1984 |
L. melanotus |
910 |
S |
k1/k2(unclear) |
3 |
Freitag et al. 1985 |
S = static; R = renewal of test medium; equi = equilibrium method (steady state);
k1/k2 = kinetic method by determining uptake rate (k1) and elimination rate (k2)
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