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EC number: 266-028-2 | CAS number: 65996-93-2 The residue from the distillation of high temperature coal tar. A black solid with an approximate softening point from 30°C to 180°C (86°F to 356°F). Composed primarily of a complex mixture of three or more membered condensed ring aromatic hydrocarbons.
- 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- Principles of method if other than guideline:
- As a summation parameter, TOC was measured rather than single PAHs.
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): pitch, coal tar, high temp (coal-tar pitch)
- Physical state: solid
- Stability under test conditions: WSF (water-soluble fraction): limited
- Storage condition of test material: room temperature, exclusion of light
- Treatment of test material prior to testing: the material was milled to a fine-granular powder (grain size < 180 µm) - Key result
- Water solubility:
- 0.242 mg/L
- Conc. based on:
- other: dissolved organic carbon (DOC)
- Loading of aqueous phase:
- 1 000 mg/L
- Incubation duration:
- >= 24 - <= 72 h
- Temp.:
- 20 °C
- pH:
- 6.8
- Remarks on result:
- other: average over 3 time intervals (24, 48, and 72 h) measured in replicate samples
- Water solubility:
- 0.215 mg/L
- Conc. based on:
- other: dissolved organic carbon (DOC)
- Loading of aqueous phase:
- 100 mg/L
- Incubation duration:
- 72 h
- Temp.:
- 20 °C
- pH:
- 6.7
- Remarks on result:
- other: mean of two replicates
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Principles of method if other than guideline:
- The analytical exercise was part of 21-d daphnia test (long-term toxicity to aquatic invertebrates, see sect. 6.1.4). Parameters determined in test medium (HPLC) were priority PAH (16 EPA + 2).
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- column elution method
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): coal tar pitch; pitch (coal tar); pitch, coal tar, high-temp
- Physical state: solid
- Density: 1.30 – 1.35 g/m³ (20 °) (DIN 51 757)
- Stability under test conditions: WSF (water-soluble fraction): limited
- Storage condition of test material: room temperature, exclusion of light
- Treatment of test material prior to testing: the test item was crushed with a mortar. Particles of the test item >125 µm were removed by sieving with an analytical sieve with a mesh width of 125 µm. - Key result
- Water solubility:
- ca. 0.8 - ca. 1.9 other: µg/L (sum of 18 PAH)
- Conc. based on:
- test mat. (dissolved fraction)
- Loading of aqueous phase:
- 100 mg/L
- Incubation duration:
- 48 h
- Temp.:
- 21 °C
- pH:
- ca. 7.3 - ca. 8
- Remarks on result:
- other: range of five replicate samples; WAF was obtained by elution of test material from a generator column for 48 hours
- Key result
- Water solubility:
- ca. 1.3 other: µg/L (sum of 18 PAH)
- Conc. based on:
- test mat. (dissolved fraction)
- Loading of aqueous phase:
- 100 mg/L
- Incubation duration:
- 48 h
- Temp.:
- 21 °C
- pH:
- ca. 7.3 - ca. 8
- Remarks on result:
- other: mean value of five replicate samples; WAF was obtained by elution of test material from a generator column for 48 hours
- Details on results:
- The maximum dissolved concentration of the test item that could be achieved under the test conditions was analysed:
The test substance concentration of the water-soluble fractions (WSFs) was determined using the fresh test medium at the beginning of each 48h test cycle (Daphnia test).
Results (sum of 18 PAH) ranged from 0.82 - 1.90 µg/L (n=5). The overall mean was 1.33 µg/L (n=5).
NOTE: For calculation of the mean value of each time interval, the measured concentrations of < LOQ(M) were set to ½ LOQ(M) = 15 ng/L. 6 - 12 out of the 18 components (PAH) were below this LOQ on occasion of analysis (Report Tab. 10).
Referenceopen allclose all
Solubility Results for Pitch, coal tar, high temp(coal-tar pitch)
(Mean values of two replicates per time interval) (data taken from Table 4 of the report, modified)
Sample |
Carbon content [mg/L] |
|
||||
Dilution water1) |
0.732 |
Mean |
Mean over time (24, 48, 72 h)4) |
Mean over time (48, 72 h)4) |
Deviation (48, 72 h) [%] |
|
1000 mg/L |
No. 1 (24 h) |
0.320 |
0.2892) |
0.242 |
||
No. 2 (24 h) |
0.258 |
|||||
No. 1 (48 h) |
0.988 |
0.2043) |
0.218 |
14.5 |
||
No. 2 (48 h) |
0.883 |
|||||
No. 1 (72 h) |
0.930 |
0.2333) |
||||
No. 2 (72 h) |
1.000 |
|||||
100 mg/L |
No. 1 (72 h) |
0.186 |
0.2152) |
|
||
No. 2 (72 h) |
0.243 |
1) Dilution water for samples 48 and 72 h at 1000 mg/L loading (measured 2010-11-15)
2) Mean values of replicates, dilution water carbon content not subtracted as dilution water carbon content was 0 mg/L (measured 2010-11-12)
3) Mean values of replicates, dilution water carbon content subtracted (measured 2010-11-15)
4) The time average over 24, 48, and 72 h was calculated, thus deviating from the study report, in which only the average over 48 and 72 h has been quoted.
Table 1: Initial concentrations of PAHs in the saturated solution of pitch, coal tar, high temp. (WSF, ng/L) (taken from Report Table 10, means recalculated for the respective time intervals)
Note: Values include background values (see blanks Table 2 below)
Sampling date |
2008-10-29 day 0 fresh medium |
2008-10-31 day 2 fresh medium |
2008-11-04 day 6 fresh medium |
2008-11-14 day 16 fresh medium |
2008-11-16 day 18 fresh medium |
Mean1) [ng/L] |
Naphthalene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
Acenaphthylene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
1-Methylnaphthalene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
32.5 |
< LOQ |
2-Methylnaphthalene |
< LOQ |
< LOQ |
43.1 |
< LOQ |
63.9 |
< LOQ |
Acenaphthene |
30.7 |
< LOQ |
84.5 |
54.1 |
132 |
63.3 |
Fluorene |
< LOQ |
< LOQ |
49.8 |
91.0 |
98.9 |
53.9 |
Phenanthrene |
247 |
153 |
296 |
185 |
380 |
252 |
Anthracene |
53.0 |
31.1 |
72.5 |
40.9 |
82.3 |
56 |
Fluoranthene |
395 |
195 |
379 |
176 |
445 |
318 |
Pyrene |
326 |
158 |
297 |
141 |
280 |
240 |
Benz[a]anthracene |
102 |
52.6 |
78.8 |
35.7 |
90.3 |
71.9 |
Chrysene |
95.2 |
50.4 |
69.8 |
36.0 |
91.3 |
80.1 |
Benzo[b]fluoranthene |
44.4 |
< LOQ |
42.3 |
< LOQ |
49.5 |
33.2 |
Benzo[k]fluoranthene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
Benzo[a]pyrene |
47.0 |
< LOQ |
47.8 |
< LOQ |
52.0 |
35.4 |
Dibenz[ah]anthracene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
Benzo[ghi]perylene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
Indeno[1,2,3-cd]pyrene |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
< LOQ |
Sum of 18 PAHs |
1475 |
820 |
1566 |
910 |
1898 |
1330 |
LOQ = Limit of quantification of the analytical method (30 ng/L for each analyte)
1) For calculation of the mean value, the measured concentrations < LOQ were set to ½ LOQ (15 ng/L).
Table 2: Concentrations of PAHs in the blank controls (taken from Report, Table 11) (WSF, ng/L)
Sampling date |
2008-10-29 day 0 fresh medium |
2008-10-31 day 2 fresh medium |
2008-11-04 day 6 fresh medium |
2008-11-14 day 16 fresh medium |
2008-11-16 day 18 fresh medium |
Naphthalene |
< 30 % LOQ |
15.1 |
10.6 |
19.4 |
14.6 |
Acenaphthylene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
1-Methylnaphthalene |
< 30 % LOQ |
11.3 |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
2-Methylnaphthalene |
12.0 |
20.1 |
14.0 |
23.1 |
23.3 |
Acenaphthene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Fluorene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
136 |
35.3 |
Phenanthrene |
16.9 |
45.6 |
< 30% LOQ |
13.4 |
26.4 |
Anthracene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Fluoranthene |
11.1 |
15.3 |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Pyrene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Benz(a)anthracene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Chrysene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Benzo(b)fluoranthene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Benzo(k)fluoranthene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Benzo(a)pyrene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Dibenz(a,h)anthracene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Benzo(ghi)perylene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Indeno(1,2,3-cd)pyrene |
< 30 % LOQ |
< 30 % LOQ |
< 30% LOQ |
< 30 % LOQ |
< 30 % LOQ |
Sum of 18 PAHs [ng/L] |
40.0 |
107 |
24.6 |
192 |
100 |
LOQ = Limit of quantification of the analytical method (30 ng/L for each analyte), values below LOQ are given in bold italics.
Description of key information
At a loading of 1000 mg pitch/L, the mean TOC of the water-soluble fraction (WAF) was 0.242 mg/L. at 20 °C. A total of 0.8 to 1.4 µg/L was found in the WAF of a loading of 100 mg/L at 21 °C, related to the 16 EPA PAHs.
Key value for chemical safety assessment
- Water solubility:
- 0.002 mg/L
- at the temperature of:
- 20 °C
Additional information
The stated water solubility relates to the marker substance, benzo[a]pyrene (EU 2008, Tab. 1.6). Water solubility of pitch, coal tar, high-temp. is different and depends on the load of the solution (see aside).
Sources:
EU (2008) Coal-Tar Pitch, high temperature - Risk Assessment. European Union Risk Assessment Report, The Netherlands [URL: https://echa.europa.eu/documents/10162/433ccfe1-f9a5-4420-9dae-bb316f898fe1]
According to EU 2008, presented data from:
Mackay D, Shiu WY, Ma KC (1992). lllustrated Handbook of Physical-Chemical Properties and Environmental Fate of Organic Chemicals. Lewis Publishers, Boca Raton, FL.
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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