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EC number: 701-305-8 | CAS number: -
- 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
Key value for chemical safety assessment
Effects on fertility
Description of key information
No experimental data of reproduction toxicity is available on Pitch, coal tar, high-temp., < 1% 4- to 5-membered condensed ring aromatic hydrocarbons [EC no. 701-305-8] (CTPhtht) itself. Benzo[a]pyrene (BaP), classified as a reprotoxin, is a key constituent of up to 0.1% in CTPhtht, and thus serves as determinant for classification of CTPhtht for this endpoint.
Link to relevant study records
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Pregnant mice were treated with graduate doses of Benzo(a)pyrene from day 7 through day 16 of gestation. Litters were monitored with regard to viability of litter, litter size, and mean pup weight development from parturition up to day 42 of life. At 7 or 8 weeks of age, F1 animals treated prenatally were introduced into a breeding study. Treated males were mated with untreated females and treated females with untreated males respectively. Reproductive performance was examined for five mating periods (treated males) and for a 6 month mating period (treated females).
- GLP compliance:
- no
- Limit test:
- no
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Labs. Inc., Wilmington, MA
- Age at study initiation: adult animals (P); 7 to 8 weeks (F1, breeding study)
- Weight at study initiation: mean pup weight (F1) at day 42 post partum 26.8 to 29.9 g
- Fasting period before study: no data
- Housing: no data
- Diet (e.g. ad libitum): Purina lab chow, ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 1 week - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS
- suspension in vehicle (corn oil)
VEHICLE
- Amount of vehicle (if gavage): 0.2 ml - Details on mating procedure:
- PARENTAL MATING
- M/F ratio per cage: 1/3 (proven breeder males with mice that had at least one litter)
- Length of cohabitation: no data
MATING OF F1 GENERATION (males treated before in utero)
- M/F ratio per cage: 1/2
- Length of cohabitation: 5 d
- Proof of pregnancy: vaginal plug referred to as day 1 of pregnancy
- Further matings: yes; as general approach, mating was replicated five times each with two new virgin mice
- After successful mating each pregnant female was caged (how): no data
- Any other deviations from standard protocol: pregnant females were allowed to deliver and fertility parameters were recorded
MATING OF F1 GENERATION (females treated before in utero)
- M/F ratio per cage: 1/1 (female housed continuously with one proven breeder male)
- Length of cohabitation: 6 month
- Proof of pregnancy: vaginal plug referred to as day 1 of pregnancy
- After 30 days of unsuccessful pairing replacement of first male by another male with proven fertility
- After successful mating each pregnant female was caged (how): no data
- Any other deviations from standard protocol: pregnant females were allowed to deliver and fertility parameters were recorded - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Pregnant mice of P generation were treated from day 7 through day 16 of gestation.
P generation males and F1 generation animals (males and females) did not get any treatment. - Frequency of treatment:
- daily
- Details on study schedule:
- - F1 animals (males and females, exposed to BaP in utero (treatment of P generation females) for 10 days) were mated at the age of 7 to 8 weeks with untreated mice of the opposite sex. F1 animals not selected for the breeding study were sacrificed.
- Remarks:
- Doses / Concentrations:
0, 10, 40, and 160 mg/kg bw /day
Basis: nominal conc. - No. of animals per sex per dose:
- Parental animals (only females treated)
0 10 40 160 mg/kg bw/day
60 30 60 30
F1 animals (breeding study)
males 45 25 45 20 (exposure only in utero) (mated with untreated females)
females 35 35 55 20 (exposure only in utero) (mated with untreated male) - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: based on preliminary study
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: no data
DETAILED CLINICAL OBSERVATIONS: no
BODY WEIGHT: no data - Oestrous cyclicity (parental animals):
- no data
- Sperm parameters (parental animals):
- Parameters examined in F1 male generation:
testis weight (10 animals) - Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: yes
- 8 pups/litter, 4 of each sex as nearly as possible; excess pups were killed and discarded
PARAMETERS EXAMINED
- The following parameters were examined in P offspring:
- number of pups, presence of gross anomalies (day 1); sex and weight of pups (day 4); viable litters, mean litter size, mean pup weight (day 4, 20, 42 post partum)
- The following parameters were examined in F1 offspring:
- number of pups, presence of gross anomalies (day 1); sex and weight of pups (day 4); weight and gross examination (day 20 post partum)
GROSS EXAMINATION OF DEAD PUPS:
- no data - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: no data
- Maternal animals: day 20 post partum
GROSS NECROPSY:
- No examination
HISTOPATHOLOGY / ORGAN WEIGHTS
- No examination - Postmortem examinations (offspring):
- ANIMALS NOT USED FOR BREEDING
- The P offspring not selected as F1 parental animals were sacrificed at 7 to 8 weeks of age. F1 offspring was sacrificed on day 20 post partum. No postmortem examinations (macroscopic and/or microscopic examinations) were conducted for these animals with the exception given below.
- From the 0, 10, and 40 mg BaP exposure group, 10 animals of either sex were sacrificed at 6 weeks of age and gross necropsy was performed.
MALE BREEDING STUDY
- No information on males
- Pregnant females were sacrificed 14 days after separation from the males (days 14-19 of gestation). Number of implants, foetuses, and resorptions were recorded
FEMALE BREEDING STUDY
- Females were left with a proven breeder male until the conclusion of the study. No postmortem examination of dams is recorded.
HISTOPATHOLOGY / ORGAN WEIGTHS
- 10 F1 male and female mice exposed to 0, 10, and 40 mg B(a)P/kg bw/day (treatment of parental females from day 7 through 16 of gestation) were subject to gross necropsy at 6 weeks of age (see above).
- Reproductive tissues were removed, trimmed, weighed (testes only), fixed in alcohol-formalin-acetic acid (AFA), sectioned, stained with Harris's hematoxylin and eosin, and prepared for microscopic examination.
- The gonads of each animal were sectioned transversely through the longest diameter of the organ. As observed lesions were approximately equal in number and uniformly distributed throughout the section, additional serial sections were deemed unnecessary. - Statistics:
- Data on pregnancy maintenance and foetal survival were analysed for statistical significance by appropriate nonparametric procedures (Siegel S. 1956, Nonparametric Statistics for the Behavioral Sciences. McGraw-Hill Book Co., New York).
The least significant difference method was used to analyse data on litter size and foetal and testes weights (Steel and Torrie 1960, Principle and Procedures of Statistics. McGraw-Hill Book Co., New York). - Reproductive indices:
- Fertility index: Females pregnant / females exposed to males x 100
- Reproductive function: oestrous cycle:
- not specified
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- effects observed, treatment-related
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- 160 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- reproductive performance
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 40 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- reproductive performance
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- not examined
- Remarks on result:
- not measured/tested
- Clinical signs:
- not specified
- Mortality / viability:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Sexual maturation:
- effects observed, treatment-related
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- not specified
- Histopathological findings:
- effects observed, treatment-related
- Behaviour (functional findings):
- not specified
- Developmental immunotoxicity:
- not examined
- Key result
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Sex:
- male/female
- Basis for effect level:
- other: Adverse effects on reproductive performance of the F1 animals were already observed at the lowest dose tested (10 mg/kg bw/day, exposure in utero in parental dams during day 7 through 16 of gestation)
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
- Key result
- Dose descriptor:
- LOAEL
- Generation:
- F1
- Effect level:
- 10 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Effects were examined only in F1 generation animals: body weight at day 20 and 42 post partum; organ weights (gonads) of males and females; histopathology of gonads; fertility index in the breeding study with F1 animals
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 10 mg/kg bw/day (nominal)
- System:
- male reproductive system
- Organ:
- testes
- Treatment related:
- yes
- Dose response relationship:
- yes
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 10 mg/kg bw/day (nominal)
- System:
- female reproductive system
- Organ:
- ovary
- Treatment related:
- yes
- Dose response relationship:
- yes
- Remarks on result:
- not measured/tested
- Reproductive effects observed:
- not specified
- Conclusions:
- Adverse effects on reproduction of the F1 animals (male and female breeding studies) were seen at all dose levels increasing with dose. Therefore, a NOAEL could not be derived. The LOAEL was determined to be 10 mg/kg bw/day.
Reference
In the highest dose group (160 mg/kg bw/day), percentage of pregnant females was significantly reduced (from ca. 75 to 50%).
Viability of the P generation offspring (F1 pups) was significantly reduced in the highest dose group (160 mg/kg bw/day) (about 40 to 50% - see table 1 below).
CLINICAL SIGNS (OFFSPRING)
No data on clinical observation of animals are reported
BODY WEIGHT (OFFSPRING)
At day 20 and 42 post partum, mean pup weight of F1 animals was significantly reduced (see table 1 below)
SEXUAL MATURATION (OFFSPRING)
Gonads of F1 animals were strongly impaired (reduced size and function) even at the lowest dose.
ORGAN WEIGHTS (OFFSPRING)
Testes weights of F1 males were significantly reduced already in the lowest dose group (by 40%).
GROSS PATHOLOGY (OFFSPRING)
No data reported
HISTOPATHOLOGY (OFFSPRING)
In males, increasing testicular damage was seen with increasing doses. Females exposed to BaP had no ovaries or only remnants of ovarian tissues (see below)
Effects of maternal treatment from day 7 to 16 of gestation on pregnancy and F1 offspring is displayed in the following table
|
Benzo[a]pyrene [mg/kg bw/day] |
|||
Dose |
0 (control) |
10 |
40 |
160 |
Females treated |
60 |
30 |
60 |
30 |
Females pregnant (%) |
46 (77) |
22 (73) |
46 (77) |
15 (50)* |
Parturition examination |
||||
Viable litters (%) |
46 (77) |
21 (70) |
44 (73) |
13 (43)** |
Mean litter sizea |
9.4 ± 0.6 |
8.6 ± 0.8 |
10.5 ± 0.5 |
8.8 ± 0.9 |
4 Day examination |
||||
Viable litters |
45 |
20 |
42 |
12 |
Mean litter sizea |
9.5 ± 0.6 |
8.6 ± 0.7 |
10.5 ± 0.5 |
8.3 ± 1.0 |
Mean pup weight [g] |
2.7 ± 0.02 |
2.8 ± 0.04 |
2.5 ± 0.02 |
2.2 ± 0.04 |
20 Day examination |
||||
Viable litters (%) |
45 (75) |
20 (67) |
40 (67) |
10 (33)** |
Mean litter sizea/b |
7.1 ± 0.3 |
7.0 ± 0.5 |
7.5 ± 0.2 |
6.5 ± 0.6 |
Mean pup weight [g] |
11.2 ± 0.1 |
11.6 ± 0.1 |
10.4 ± 0.1** |
9.7 ± 0.2** |
42 Day examination |
||||
Viable litters (%) |
45 (75) |
20 (67) |
40 (67) |
10 (33)** |
Mean litter sizea/b |
7.0 ± 0.3 |
6.8 ± 0.5 |
7.1 ± 0.2 |
5.9 ± 0.5 |
Mean pup weight [g] |
29.9 ± 0.2 |
28.2 ± 0.3** |
28.0 ± 0.2** |
26.8 ± 0.4** |
aMean number of live pups per viable litter ± SEM
bAll litters were standardised t 8 pups per litter on Day 4
*Significantly different from controls (P<0.05)
**Significantly different from controls (P<0.01)
BaP was not toxic to mothers or foetuses at any dose tested. All litters appeared normal by gross observation. But pregnancy maintenance was reduced by ca. 25% at the 160 mg/kg bw/day dose level, and there was a significant decrease at 20 and 42 days of age in weights of pups from treated dams.
Reproductive performance of male and female F1 mice exposed prenatally to BaP (from day 7 through day 16 of gestation) (mean ± SEM)
|
Benzo[a]pyrene [mg/kg bw/day] |
|||
Dose |
0 (control) |
10 |
40 |
160 |
Male breeding study |
||||
Number F1 males testeda |
45 (45) |
25 (20) |
45 (3) |
20 (0) |
Fertility indexb |
80.4 |
52.0* |
4.7** |
0.0** |
Mean litter size |
11.0 ± 0.1 |
10.7 ± 0.2 |
10.8 ± 0.6 |
--- |
Female breeding study |
||||
Number F1 females testedc |
35 |
35 |
55 |
20 |
Fertility indexb |
100.0 |
65.7** |
0.0** |
0.0** |
Mean litter size |
12.9 ± 0.2 |
10.4 ± 0.4** |
--- |
--- |
aBeginning at 7 weeks of age, each F1 male was exposed to 10 untreated females over a period of 25 days.
bFertility index: Females pregnant / females exposed to males x 100
cBeginning at 6 weeks of age, each F1 female was cohabitated continuously with an untreated male for a period of 6 month.
*Significantly different from controls (P<0.05)
**Significantly different from controls (P<0.01)
Adverse effects on reproduction of the F1 animals (male and female breeding studies) were seen at all dose levels increasing with dose. At the highest dose (160 mg/kg bw/day), all of the male mice were infertile and no litter was produced. For females, animals of the two highest dose groups (40 and 160 mg/kg bw/day) did not generate any offspring. At the lowest dose (10 mg/kg bw/day), fertility and ability to produce offspring was already reduced by ca. 20 to 30%.
There were no gross abnormalities in F2 offspring from the F1 reproduction studies, and there were no significant differences among treatment groups in F2 pup mean body weights at 4 and 20 days of age in the female breeding study.
The most obvious effect of prenatal exposure to BaP was a dramatic decrease in the size of the gonads. Paired testes weights were significantly reduced, and testes from animals exposed in utero to 10 and 40 mg BaP weighed only ca. 60% and 18% of the testes weights from control animals, respectively.
Histologic examination of gonadal tissue sections revealed significant alterations following exposure to BaP as well. In males, increasing testicular damage was seen with increasing doses. In the low dose group (10 mg/kg bw/day), testes of all males showed evidence of tubular injury, but each animal also had some seminiferous tubules that displayed active spermatogenesis. In the 40 mg/kg bw/day group, tubules were smaller compared to control animals and they were empty except for a basal layer of cells. Females exposed to BaP had no ovaries or only remnants of ovarian tissues. Ovarian tissue was hyperplastic with very few follicles and corpora lutea. At higher doses (40 mg/kg bw/day) no evidence of folliculogenesis could be observed. Ovarian tissue fragments consisted of lutein cells, medullary cords, and very little interstitial tissue.
Effect on fertility: via oral route
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LOAEL
- 10 mg/kg bw/day
- Study duration:
- subacute
- Species:
- mouse
- Quality of whole database:
- acceptable; yet, of limited relevance for the evaluation of the inherent properties of the target compound, CTPhtht, since the analogue approach is worst-case; but applicable for classification of BaP-containing mixtures.
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Studies on reproductive toxicity using Pitch, coal tar, high-temp., < 1% 4- to 5-membered condensed ring aromatic hydrocarbons [EC no. 701-305-8] (CTPhtht) are not available. In a fertility study with benzo[a]pyrene following no guideline (exposure of pregnant dams from day 7 to day 16 of gestation, monitoring of reproductive success and development of F1 offspring and reproductive performance of F1 males and females), adverse effects on fertility were observed even at the lowest concentration tested (10 mg/kg bw/d). A NOAEL was not identified.
Justification for classification or non-classification
Benzo[a]pyrene is classified as reproductive toxicant Cat. 1B. Given a maximum content of approx. 0.10 % of benzo[a]pyrene and in analogy of the precursor compound Pitch, coal tar (CTPht), the target substance Pitch, coal tar, high-temp., < 1% 4- to 5-membered condensed ring aromatic hydrocarbons [EC no. 701-305-8] (CTPhtht) has been classified as reproductive toxicant Cat. 1B by the registrant.
Additional information
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