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EC number: 210-236-8 | CAS number: 610-81-1
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 11 May 2004 To 2 June 2005
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 4-amino-3-nitrophenol
- EC Number:
- 210-236-8
- EC Name:
- 4-amino-3-nitrophenol
- Cas Number:
- 610-81-1
- Molecular formula:
- C6H6N2O3
- IUPAC Name:
- 4-amino-3-nitrophenol
- Test material form:
- solid: particulate/powder
- Remarks:
- Dark red powder
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: supplied by the sponsor, batch no. 0508916
- Expiration date of the lot/batch: September 2005
- Purity test date: 31 August 2004
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: in glass flask, stored at +4°C, protected from light and under nitrgen gas
- Stability under test conditions: not specified
- Solubility and stability of the test substance in the solvent/vehicle: solubility : <1g/L at 25°C ; stability : deviations of formulation were within the acceptable range of ±10% (maximal deviation : 9%)
- Reactivity of the test substance with the solvent/vehicle of the cell culture medium: not specified
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
Before preparation, the vehicle was degassed by sonication for at least 15 minutes and then saturated with nitrogen gas, and kept under nitrogen atmosphere for 15 minutes.
The test item was administered as a suspension in the vehicle. The test item was ground to fine powder using a mortar and pestle, suspended in the vehicle at the concentrations of 1, 4 and 80 mg/mL and then homogenized using a magnetic stirrer.
The test item dosage forms were prepared weekly under nitrogen atmosphere and were stored at +4°C, protected from light (using a glass beaker covered with aluminum foil) and under nitrogen atmosphere until delivery.
Test animals
- Species:
- rat
- Strain:
- Crj: CD(SD)
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories
- Age at study initiation: 10-11 weeks old
- Weight at study initiation: 267g (225 to 316g)
- Fasting period before study: not specified
- Housing: The animals were housed individually in suspended wire-mesh cages (43.0 x 21.5 x 18.0 cm)
- Diet (e.g. ad libitum): The animals had free access to A04 C pelleted maintenance diet, batch No. 40227 (SAFE, Villemoisson, Epinay-sur-Orge, France) distributed weekly
- Water (e.g. ad libitum):The animals had free access to bottles containing tap water (filtered with a 0.22 µm filter).
- Acclimation period:a 5-day acclimation period to the conditions of the study preceded the beginning of the mating period
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22±2°C
- Humidity (%): 50±20%
- Air changes (per hr): about 12 cycles/hour of filtered, non-recycled air.
- Photoperiod (hrs dark / hrs light):
IN-LIFE DATES: From: 11 may 2004 To: 11 June 2004
Administration / exposure
- Route of administration:
- oral: gavage
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Before preparation, the vehicle was degassed by sonication for at least 15 minutes and then saturated with nitrogen gas, and kept under nitrogen atmosphere for 15 minutes.
The test item was administered as a suspension in the vehicle. The test item was ground to fine powder using a mortar and pestle, suspended in the vehicle at the concentrations of 1, 4 and 80 mg/mL and then homogenized using a magnetic stirrer
VEHICLE
- Justification for use and choice of vehicle (if other than water): no justification
- Concentration in vehicle: 1,4 and 80 mg/ml
- Amount of vehicle (if gavage): 5mL/kg/day
- Lot/batch no. (if required): carboxymethylcellulose, batch No. 101K0185, supplied by Sigma - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Before the start of treatment, the suitability of the proposed preparation procedure was determined by analysis of the homogeneity, stability and concentration of the dosage forms, which were prepared using this procedure. Deviations of formulation were within the acceptable range of ±10% (maximal deviation : 9%).
- Details on mating procedure:
- - Impregnation procedure: cohoused
- If cohoused:
- M/F ratio per cage: 1/1
- Length of cohabitation: overnight
- Further matings after two unsuccessful attempts: no
- Verification of same strain and source of both sexes: yes
- Proof of pregnancy: vaginal plug and/or sperm in vaginal smear referred to as day 0 - Duration of treatment / exposure:
- during the day 6 to 20 of gestation
- Frequency of treatment:
- once daily
- Duration of test:
- until the day 20 of gestation
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Dose / conc.:
- 5 mg/kg bw/day (nominal)
- Dose / conc.:
- 20 mg/kg bw/day (nominal)
- Dose / conc.:
- 400 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 24 females were used per dose group
- Control animals:
- yes
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The selection of dose-levels for the present study were selected in agreement with the Sponsor based on the results of a previous study (Toxicol Laboratories Ltd, LRL/13/91, 1991) performed at 100, 250 and 600 mg/kg/day.
- Rationale for animal assignment (if not random): the animals were allocated to the groups, according to a stratification procedure based on body weight, recorded on day 0 p.c., to ensure comparatively similar mean body weights in the groups.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least twice a day during the treatment period, at least once a day on other days.
- Cage side observations checked : for mortality or signs of morbidity.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: From arrival, the animals were observed at least once a day as part of routine examinations. From the start of the treatment period, each animal was observed at least once a day, at approximately the same time for the recording of clinical signs.
BODY WEIGHT: Yes
- Time schedule for examinations: The body weight of each female was recorded on days 0, 3, 6, 9, 12, 15, 18 and 20 post-coitum
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
The quantity of food consumed by each female was recorded for the following intervals:
days 0-3, 3-6, 6-9, 9-12, 12-15, 15-18 and 18-20 post-coitum.
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day # 20
- Organs examined: examination of the principal thoracic and abdominal organs.
- 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: Any uterine horns without visible implantation sites were immersed in an aqueous solution of ammonium sulphide (Salewski) to reveal the presence of uterine scars.
A gross evaluation of placentas was also undertaken - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: half per litter
- Skeletal examinations: Yes: half per litter
- Head examinations: No - Statistics:
- Mean values were compared by one-way analysis of variance and the Dunnett test (mean values being considered as normally distributed and variances being considered as homogeneous).
Percentage values were compared by the Fisher exact probability test. - Historical control data:
- Historical control datas were provided in the report
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- No clinical signs were noted at 5 mg/kg/day.
At 20 and 400 mg/kg/day, orange colored urines was noted in all animals. Coloration of extremities and fur was also recorded in all animals given 400 mg/kg/day. These findings, which were considered to be evidence of the renal elimination of the test item-related material, were observed many days during the dosing period and suggested systemic exposure to test item following oral administration.
Furthermore, ptyalism was noted in 3/24 females given 400 mg/kg/day, from days 17 or 19 post-coitum until the last dosing.
The above cited findings were not considered to represent adverse effects. - Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, non-treatment-related
- Description (incidence and severity):
- The fluctuations noted in body weight, body weight gain and net body weight change were minor, not statistically significant and not dose-related, consequently, they were not considered treatment-related.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- The findings recorded at necropsy were low in incidence and concerned two animals in each of the control, 5 and 20 mg/kg/day groups. As no necropsy findings were noted at the high dose-level, the observed findings were considered to be of spontaneous origin.
Maternal developmental toxicity
- Pre- and post-implantation loss:
- effects observed, non-treatment-related
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Effects on pregnancy duration" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsMaternalAnimals.MaternalDevelopmentalToxicity.EffectsOnPregnancyDuration): no effects observed - Changes in number of pregnant:
- not examined
- Description (incidence and severity):
- All females were pregnant with live fetuses except one (E29103) in the group given 20 mg/kg/day.
- Details on maternal toxic effects:
- At all dose-levels, the number of corpora lutea and implantation sites were similar to controls. The only finding of statistical significance was the higher total pre-implantation loss noted at 5 mg/kg/day mainly due to one female; it was therefore considered to be incidental.
The mean post-implantation loss and the mean number of live fetuses were unaffected by the treatment. No dead fetuses were noted in any group.
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 400 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- clinical signs
- gross pathology
- maternal abnormalities
- mortality
- pre and post implantation loss
Maternal abnormalities
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- The fetal weight was unaffected by treatment.
Migrated Data from removed field(s)
Field "Fetal/pup body weight changes" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.FetalPupBodyWeightChanges): no effects observed - Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in postnatal survival:
- no effects observed
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Except for one fetus with a gastroschisis (as a malformation) at 20 mg/kg/day and another fetus with a malrotated paw (as a variation) at 400 mg/kg/day, no malformations or variations were noted. These isolated findings were considered to be unrelated to treatment.
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no soft tissue malformations in any group.
The nature and incidence of the observed soft tissue variations were minor, they were randomly distributed, sometimes with a higher incidence in controls than in treated groups. They were consequently considered not to be treatment-related.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 400 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- external malformations
- skeletal malformations
- visceral malformations
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Table: 1
CLINICAL SIGNS (Summary table/Females/Pregnancy period)
------------------------------------------------------------------------------------------------------------------------------------
Dose:(mg/kg/day) 0 5 20 400
------------------------------------------------------------------------------------------------------------------------------------
Mortality
FINAL SACRIFICE 24 24 24 24
Secretion/Excretion |
|
|||
ORANGE COLOURED URINE |
0 |
0 |
24 |
24 |
PTYALISM |
0 |
0 |
0 |
3 |
Abscess/Nodosities
NODOSITIES ON HEAD 1 0 0 1
|
Normal
NOREMARKABLEOBSERVATIONS 23 24 0 0
Table 2 BODY WEIGHT (Mean values/grams/Females/Pregnancy period)
------------------------------------------------------------------------------------------------------------------------------------
Dose:(mg/kg/day) 0 5 20 400
------------------------------------------------------------------------------------------------------------------------------------
DAY 0 |
MEAN |
222 d |
224 |
226 |
226 |
|
S.D. |
19 |
18 |
16 |
15 |
|
N |
24 |
24 |
23 |
24 |
DAY 3 |
MEAN |
245 d |
248 |
249 |
249 |
|
S.D. |
21 |
19 |
15 |
17 |
|
N |
24 |
24 |
23 |
24 |
DAY 6 |
MEAN |
266 d |
267 |
268 |
269 |
|
S.D. |
21 |
19 |
17 |
19 |
|
N |
24 |
24 |
23 |
24 |
DAY 9 |
MEAN |
281 d |
281 |
283 |
281 |
|
S.D. |
22 |
20 |
17 |
19 |
|
N |
24 |
24 |
23 |
24 |
DAY 12 |
MEAN |
300 d |
300 |
303 |
300 |
|
S.D. |
24 |
22 |
18 |
21 |
|
N |
24 |
24 |
23 |
24 |
DAY 15 |
MEAN |
323 d |
319 |
323 |
320 |
|
S.D. |
25 |
23 |
20 |
23 |
|
N |
24 |
24 |
23 |
24 |
DAY 18 |
MEAN |
362 d |
361 |
363 |
360 |
|
S.D. |
29 |
29 |
22 |
28 |
|
N |
24 |
24 |
23 |
24 |
DAY 20 |
MEAN |
396 d |
394 |
399 |
395 |
|
S.D. |
35 |
31 |
23 |
30 |
|
N |
24 |
24 |
23 |
24 |
------------------------------------------------------------------------------------------------------------------------------------
Statisticalkey:d=ANOVA+Dunnett-test
Table: 3
HYSTERECTOMY DATA (Summary table)
------------------------------------------------------------------------------------------------------------------------------------
Dose:(mg/kg/day) 0 5 20 400
------------------------------------------------------------------------------------------------------------------------------------
PregnantFemalesAliveatTerm |
N |
24 |
24 |
23 |
24 |
with Total Resorptions |
N |
0 |
0 |
0 |
0 |
withall Dead Fetuses |
N |
0 |
0 |
0 |
0 |
with Live Fetuses |
N |
24 |
24 |
23 |
24 |
Corpora Lutea |
TOTAL |
367 |
376 |
342 |
367 |
No. peranimal |
MEAN |
15.3 d |
15.7 |
14.9 |
15.3 |
|
S.D. |
1.9 |
2.2 |
2.2 |
2.3 |
Implantation Sites |
TOTAL |
354 |
348 |
322 |
348 |
No. peranimal |
MEAN |
14.8 d |
14.5 |
14.0 |
14.5 |
|
S.D. |
2.1 |
2.1 |
2.0 |
2.1 |
Preimplantation Loss |
TOTAL |
13 f |
28* |
20 |
19 |
|
% |
3.5 |
7.4 |
5.8 |
5.2 |
Fetuses |
N |
337 |
333 |
310 |
335 |
No. peranimal |
MEAN |
14.0 d |
13.9 |
13.5 |
14.0 |
|
S.D. |
2.3 |
2.4 |
2.2 |
2.3 |
Alive |
% |
100.0 |
100.0 |
100.0 |
100.0 |
Dead |
% |
0.0 |
0.0 |
0.0 |
0.0 |
Live Fetuses |
N |
337 f |
333 |
310 |
335 |
%of implantation sites |
|
95.2 |
95.7 |
96.3 |
96.3 |
No. peranimal |
MEAN |
14.0 d |
13.9 |
13.5 |
14.0 |
|
S.D. |
2.3 |
2.4 |
2.2 |
2.3 |
Dead Fetuses |
N |
0 f |
0 |
0 |
0 |
%of implantation sites |
|
0.0 |
0.0 |
0.0 |
0.0 |
No. peranimal |
MEAN |
0.0 |
0.0 |
0.0 |
0.0 |
|
S.D. |
0.0 |
0.0 |
0.0 |
0.0 |
Resorptions+Scars |
N |
17 f |
15 |
12 |
13 |
% of implantation site |
|
4.8 |
4.3 |
3.7 |
3.7 |
No. peranimal |
MEAN |
0.7 d |
0.6 |
0.5 |
0.5 |
|
S.D. |
1.0 |
0.9 |
0.7 |
1.3 |
ImplantScars N 0f 0 0 0
%ofimplantationsites 0.0 0.0 |
0.0 |
0.0 |
|||
No. peranimal |
MEAN |
0.0 |
0.0 |
0.0 |
0.0 |
|
S.D. |
0.0 |
0.0 |
0.0 |
0.0 |
Resorptions: early |
N |
17 f |
15 |
12 |
13 |
%ofimplantationsites |
|
4.8 |
4.3 |
3.7 |
3.7 |
No. peranimal |
MEAN |
0.7 d |
0.6 |
0.5 |
0.5 |
|
S.D. |
1.0 |
0.9 |
0.7 |
1.3 |
Resorptions: late |
N |
0 f |
0 |
0 |
0 |
%of implantation sites 0.0 0.0 |
0.0 |
0.0 |
|||
No. peranimal |
MEAN |
0.0 |
0.0 |
0.0 |
0.0 |
|
S.D. |
0.0 |
0.0 |
0.0 |
0.0 |
PostimplantationLoss |
TOTAL |
17 f |
15 |
12 |
13 |
%of implantation sites |
|
4.8 |
4.3 |
3.7 |
3.7 |
No. peranimal |
MEAN |
0.7 d |
0.6 |
0.5 |
0.5 |
|
S.D. |
1.0 |
0.9 |
0.7 |
1.3 |
Male Fetuses |
N |
163 f |
148 |
144 |
157 |
|
% |
48.4 |
44.4 |
46.5 |
46.9 |
Female Fetuses |
N |
174 f |
185 |
166 |
178 |
|
% |
51.6 |
55.6 |
53.5 |
53.1 |
Fetal Body Weight (g) |
MEAN |
3.73 d |
3.72 |
3.81 |
3.66 |
|
S.D. |
0.19 |
0.30 |
0.18 |
0.22 |
Male Fetuses |
MEAN |
3.83 d |
3.83 |
3.91 |
3.75 |
|
S.D. |
0.21 |
0.28 |
0.18 |
0.24 |
Female Fetuses |
MEAN |
3.63 d |
3.64 |
3.71 |
3.58 |
|
S.D. |
0.18 |
0.29 |
0.20 |
0.21 |
------------------------------------------------------------------------------------------------------------------------------------
Statisticalkey:d=ANOVA+Dunnett-testf=Fishersexacttest
Table 4 Incidence of fetal skeletal variations (%), litter incidence (%) and mean number of affected fetuses (%)
Dose-levels (mg/kg/day) |
0 |
5 |
20 |
400 |
Incomplete ossification of supra occipital bone |
|
|
|
|
.fetal incidence (%) |
0.6 [4.2] |
1.2 [8.3] |
0.6 [4.3] |
5.2 [16.7] |
.mean affected fetuses/litter (%) |
0.6 |
1.1 |
0.5 |
4.9 |
Incomplete ossification of Hyoid |
|
|
|
|
.fetal incidence (%) |
3.5 [16.7] |
3.5 [12.5] |
9.9 [34.8] |
10.3 [37.5] |
.mean affected fetuses/litter (%) |
3.4 |
3.2 |
9.5 |
9.6 |
Unossified Hyoid |
|
|
|
|
.fetal incidence(%) |
6.4[20.8] |
5.2 [12.5] |
3.7[26.1] |
1.7 [12.5] |
. mean affected fetuses/litter |
5.9 |
5.1 |
3.6 |
1.7 |
Unossified 6thsternebra |
|
|
|
|
.fetalincidence (%) |
0.6 [4.2] |
1.7 [12.5] |
1.2 [8.7] |
5.2 [25] |
.meanaffected fetuses/litter (%) |
0.5 |
2.1 |
1.3 |
5.9 |
Unossified4thmetacarpal bone |
|
|
|
|
.fetal incidence (%) |
3.5 [20.8] |
6.4 [33.3] |
1.2 [8.7] |
9.2 [25] |
.mean affected fetuses/litter (%) |
3.4 |
7.0 |
1.1 |
9.7 |
Short supernumerary 14thribs |
|
|
|
|
.fetalincidence (%) |
0.6[4.2] |
1.2[8.3] |
1.9[13.0] |
4.0[25.0] |
.meanaffected fetuses/litter (%) |
3.4 |
3.8 |
5.2 |
7.4 |
[ ]: % of litters affected, *: p<0.05.
HCD: Historical Control Data.
HCD for incomplete ossification of hyoid: mean affected fetuses/litter: minimum= 0, maximum= 19.9%. HCD forunossified6thsternebra: mean affected fetuses/litter: minimum= 0, maximum= 14.1%.
HCD for unossified 4thmetacarpal bone: mean affected fetuses/litter: minimum= 2.8, maximum= 41.1%. HCD for incomplete ossification of supraoccipital: mean affected fetuses/litter: minimum= 0, maximum=7.2%.
HCD for short supernumerary 14thribs: mean affected fetuses/litter: minimum=0.0 ,maximum= 7.6%.
Applicant's summary and conclusion
- Conclusions:
- Under the experimental condition of the study, the test item, 4-amino-3-nitrophenol (B051), batch No. 0508916, administered daily by gavage to pregnant female Sprague-Dawley rats from day 6 to 19 post-coitum was well tolerated at 5, 20 and 400 mg/kg/day.
Consequently, the No Observed Adverse Effect Level (NOAEL) for maternal and prenatal toxicity is 400 mg/kg/day. - Executive summary:
The objective of this GLP compliant study was to evaluate the potential toxic effects of the test item, 4-amino-3-nitrophenol (B051), on the pregnant female and on embryonic and fetal development following daily oral administration (gavage) to pregnant female rats, from days 6 to 19 post-coitum inclusive.
Pregnant SD rats were exposed to the 4 -amino-3 -nitrophenol daily using oral gavage administration at 0, 5, 20, and 400 mg/kg/day from day 6 through day 19 of gestation. Test Item was administered in 0.5% aqueous carboxymethylcellulose.Maternal evaluations and measurements included daily clinical signs, food intake and body weight gain. The dams were sacrificed and subjected to macroscopic examinations, gravid uterus weights were measured and foetuses removed. Typical litter parameters were recorded and foetuses were sexed, weighed and examined. Half of the foetuses were examined for soft tissue anomalies and the other half of the foetuses were examined for skeletal anomalies.
No deaths were reported and clinical signs were limited to orange coloured urine. This fact indicates a renal elimination of test article or its coloured metabolites and thus systemic exposure following oral exposure . An increase of short supernumerary rib was reported at 400 mg/kg/day in foetuses of some of the litters which was however, not statistically significant. Because the incidence (4.1%) was within the historical control range (0.0 – 7.6%) and because no foetuses had full supernumerary rib or abnormal pre-sacral vertebrae, the observation was considered not to be adverse.
Under the experimental condition of the study, the test item, 4-amino-3-nitrophenol (B051), batch No. 0508916, administered daily by gavage to pregnant female Sprague-Dawley rats from day 6 to 19 post-coitum was well tolerated at 5, 20 and 400 mg/kg/day. Consequently, the No Observed Adverse Effect Level (NOAEL) for maternal and prenatal toxicity is 400 mg/kg/day.
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