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EC number: 292-607-4 | CAS number: 90640-86-1 Distillate from the fractional distillation of coal tar of bituminous coal, with boiling range of 240°C to 400°C (464°F to 752°F). Composed primarily of tri- and polynuclear hydrocarbons and heterocyclic compounds.
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- - Soft-tissue examinations only on 1/3 instead of 1/2 of the foetuses. Post-treatment period of five days prior to caesarean sect.: Acc. to OECD TG 414 (22 Jan. 2001), dosage should cover the whole pregnancy up to 1 d prior to scheduled caesarean sect.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 83-3 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Creosote - US P1/P3
- IUPAC Name:
- Creosote - US P1/P3
- Details on test material:
- US Type P1/13 based on GC/MS (Selection of Key Compounds)
- Substance type: organic
- Physical state: liquid
Distilled Coal Tar, Complex Hydrocarbon Mixture
Component CAS-No. [%][US P1/13]
Naphthalene 91-20-3 9.0
1-Methylnaphthalene 90-12-0 2.3
2-Methylnaphthalene 91-57-6 5.1
Indene 95-13-6 0.9
Fluorene 86-73-7 4.2
Acenaphthylene 208-96-8 0.3
Acenaphthene 83-32-9 6.1
Phenanthrene 85-01-8 12.2
Anthracene 120-12-7 2.2
Fluoranthene 206-44-0 6.8
Pyrene 129-00-0 6.0
Benz[a]anthracene 56-55-3 0.5
Chrysene 218-01-9 1.5
Benzo(a)pyrene 50-32-8 0.5
Total of 5 remaining EPA-PAH: ca. 1.4
(Benzo[b]fluoranthene, 205-99-2 0.8
Benzo[k]fluoranthene, 207-08-9 0.3
Indeno[1,2,3-cd]pyrene, 193-39-5 0.1
Dibenzo[a,h]anthracene, 53-70-3 not identified
Benzo[ghi]perylene, 191-24-2 <0.1
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: SD, Crl:CD® VAF/Plus®
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Portage, Michigan, USA
- Age at study initiation: Approx. 13 weeks
- Weight at study initiation:210 – 278 g
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- VEHICLE
- Concentration in vehicle: 2.5, 7.5, 22.5 mg/ml
- Amount of vehicle (if gavage):10 ml/(kg bw*d) - Analytical verification of doses or concentrations:
- no
- Details on mating procedure:
- Mating period: Until detection of copulatory plug (= day 0 of gestation)
- Duration of treatment / exposure:
- Day 6-15 of gestation
- Frequency of treatment:
- 1x/d
- Duration of test:
- Duration of exposure: Day 6-15 of gestation
Postexposure period: Day 16-20 of gestation.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
25, 50, 175 mg/(kg bw*d)
Basis:
actual ingested
- No. of animals per sex per dose:
- 30 mated females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- --
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Daily on days 6-20
BODY WEIGHT: Yes
- Time schedule for examinations: Days 0, 6, 9, 12, 16 and 20
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes, days 0, 6, 9, 12, 16 and 20
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / No data
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study) No
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 20 - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: Number and location of viable and non-viable fetuses - Fetal examinations:
- - External examinations: Yes
- Soft tissue examinations: Yes
- Skeletal examinations: Yes
- Head examinations: No data
Litter size, number of dead foetuses, foetal weight, sex ratio, external alterations - Statistics:
- --
- Indices:
- --
- Historical control data:
- --
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
175 mg/(kg*d) dosage level: weak maternal toxicity as evidenced by increased hair loss, body weight loss during the first subinterval of treatment (gestation days 6-9), inhibition in body weight gain during the treatment period (days 6-16) and throughout gestation (until day 20), and decreased food consumption. There was a decreasing trend only without clear statistical significance.
50 mg/(kg*d) dosage level or lower: No evidence of maternal toxicity.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- LOAEL
- Effect level:
- 175 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
Developmental toxicity at the 175 mg/(kg*d) dosage level: Increased incidence in post-implantation loss (including three whole litter resorptions vs. one litter resorbed in the vehicle control and none in the other treated groups), and reduced number of live foetuses. No adverse effect was demonstrated for late intrauterine development of live foetuses at any dose.
No evidence of developmental toxicity was observed at the 50 mg/(kg*d) dosage level or lower.
One, six, seven, and seven foetuses showed malformations in one, three, six, and five litters for the control, low-, mid-, and high-dose groups, respectively. The incidences for the mid-, and high-dose levels were significantly higher than for the control group. Most of the observed malformations are fairly common in rats and the values obtained for the eye malformations in this study were within historical control range. After factoring out these common eye abnormalities, each type of the remaining malformations occurred in only one or two instances per group. Thus, the malformations were not considered to be test-article related.
Developmental variations that occurred did not follow a dose-related pattern.
Effect levels (fetuses)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: embryotoxicity
- Dose descriptor:
- LOAEL
- Effect level:
- 175 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: embryotoxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 175 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: fetotoxicity
- Dose descriptor:
- LOAEL
- Effect level:
- > 175 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: fetotoxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 175 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: teratogenicity
- Dose descriptor:
- LOAEL
- Effect level:
- > 175 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: teratogenicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Table forMaternal Effects |
||||||
Parameter |
Control data |
25 mg/(kg*d) |
50 mg/(kg*d) |
175 mg/(kg*d) |
Dose-response |
|
historical |
study |
|||||
Number of dams examined |
716 |
30 |
30 |
30 |
30 |
|
Pregnant females |
27 |
20 |
23 |
23 |
||
Pregnancies [%] |
90.0 |
66.0 |
76.0 |
76.0 |
– |
|
Clinical findings during application of test substance |
13 |
15 |
11 |
17 |
– |
|
Mortality of dams [%] |
0 |
0 |
0 |
0 |
0 |
– |
Body weight gain |
||||||
day 0-6 |
34 |
34 |
32 |
30 |
– |
|
day 6-9 |
2 |
5 |
3 |
-2 |
– |
|
day 9-12 |
12 |
12 |
13 |
12 |
– |
|
day 12-16 |
28 |
21 |
25 |
21 |
– |
|
day 16-20 |
57 |
65 |
64 |
51 |
– |
|
day 6-16 |
42 |
38 |
40 |
31 |
– |
|
day 0-20 |
143 |
133 |
137 |
136 |
112 |
– |
Final dam weight change minus weight of uterus |
62 |
64 |
67 |
66 |
61 |
– |
Food consumption [g/animal/day] |
||||||
day 0-6 |
21.2 |
21.0 |
20.2 |
20.5 |
– |
|
day 6-9 |
14.6 |
16.7 |
14.4 |
12.9 |
– |
|
day 9-12 |
14.1 |
15.5 |
14.1 |
13.6 |
– |
|
day 12-16 |
17.9 |
15.0 |
12.6* |
9.8** |
+ |
|
day 16-20 |
25.5 |
28.6 |
29.5 |
30.4 |
– |
|
day 6-16 |
15.7 |
15.7 |
13.6 |
11.9** |
+ |
|
day 0-20 |
19.4 |
19.9 |
18.8 |
18.2 |
– |
|
Necropsy findings in dams dead before end of test |
No deaths occurred before end of test. |
|||||
* Significantly different from controls, p ≤ 0.05 |
Table forDevelopmentalEffects Litter response (Caesarean section data) |
||||||
Parameter |
Controldata |
25 mg/kg/ day |
50 mg/kg/ day |
175 mg/kg/ day |
Dose-response |
|
historical |
study |
|||||
Corpora lutea mean/dam |
16.8 |
16.6 |
16.0 |
16.3 |
16.0 |
– |
Implantations mean/dam |
15.0 |
14.2 |
13.8 |
14.6 |
12.9 |
– |
Resorptions total/number of dams |
850/708 |
31/27 |
17/20* |
25/23 |
59/23* |
+ |
Number of foetuses/dam |
13.0 |
13.0 |
13.5 |
10.3 |
– |
|
Pre-implantation loss [%] |
11.6 |
13.8 |
10.6 |
12.2 |
– |
|
Post-implantation loss [%] |
7.3 |
8.1 |
6.2 |
7.4 |
19.9 |
+ |
Total number of litters |
26 |
20 |
23 |
20 |
– |
|
Foetuses / litter |
13.0 |
13.0 |
13.5 |
10.3 |
– |
|
Live foetuses / litter ratio |
13.9 |
13.0 |
13.0 |
13.5 |
10.3 |
– |
Dead foetuses / litter ratio |
0 |
0 |
0 |
0 |
– |
|
Foetus weight (mean) [g] |
3.4 |
3.3 |
3.5 |
3.3 |
3.2 |
– |
Male foetuses |
3.4 |
3.6 |
3.4 |
3.3*1) |
+ |
|
Female foetuses |
3.3 |
3.3 |
3.2 |
3.2 |
– |
|
Uterine weight (mean) [g] |
76.3 |
72.0 |
69.5 |
70.0 |
61.4 |
– |
Crown-rump length (mean)[mm] |
35 |
36 |
35 |
35 |
– |
|
Foetal sex ratio [state ratio m/f] |
0.982 |
1.108 |
0.904 |
1.006 |
1.135 |
– |
* Significantly different from controls, p ≤ 0.05 1)questionable, no effect on crown length, see also female values, considered biologically irrelevant |
||||||
Table forMorphologicalEffects Examination of the foetuses(Report, Tab. 9 + 10, p. 42/43) |
||||||
Parameter |
Controldata |
25 mg/kg/ day |
50 mg/kg/ day |
175 mg/kg/ day |
Dose-response |
|
historical |
study |
|||||
External malformations*[%] |
0.20 |
0.00 |
0.77 |
2.891) |
1.27 |
– |
Skeletal malformations*[%] |
0.93 |
0.00 |
0.81 |
4.351) |
1.72 |
– |
Visceral malformations*[%] |
0.41 |
0.58 |
2.21 |
1.33 |
2.50 |
– |
Fetuses with malformations [%]* |
0.58 |
3.8 |
3.92) |
5.5 |
||
External variations*[%] |
0.01 |
0.00 |
0.00 |
0.00 |
0.00 |
– |
Skeletal variations*[%] |
34.4 |
36.7 |
50.4 |
49.7 |
43.1 |
– |
Visceral variations*[%] |
1.44 |
10.5 |
11.0 |
7.33 |
1.67 |
– |
*Figures are not given in the original study but calculated from the number of observations and the number of examined foetuses in the respective category.
1)The relatively high incidences are only determined by an accumulation of 11 different skeletal and external malformations within one foetus from doe No. 56513 (Report, Appendix C, p. 100).
2)Because of multi-fold malformations observed in two foetuses (one with 4 and a second with 2 defects), the percentage of the number of animals with malformations is lower than the total percentage of malformations (comp. Report,Appendix C, p. 98ff). Four other foetuses carried only one structural defect as in the other dose groups.Applicant's summary and conclusion
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