Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 282-941-9 | CAS number: 84473-86-9
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- one-generation reproductive toxicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- Data is from peer reviewed journal
Data source
Reference
- Reference Type:
- publication
- Title:
- A TERATOGENICITY STUDY OF PHLOXINE B IN ICR MICE
- Author:
- M. SENO, S. FUKUDA and H. UMISA
- Year:
- 1 984
- Bibliographic source:
- Fd Chem. Toxic. Vol. 22, No. 1 pp. 55-60, 1984
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: As mentioned below
- Principles of method if other than guideline:
- one-generation toxicity study of Phloxine B in Jcl:ICR Mice
- GLP compliance:
- not specified
- Limit test:
- no
- Justification for study design:
- No data available
Test material
- Reference substance name:
- 3,4,5,6-tetrachloro-2-(1,4,5,8-tetrabromo-6-hydroxy-3-oxoxanthen-9-yl)benzoic acid
- EC Number:
- 242-355-6
- EC Name:
- 3,4,5,6-tetrachloro-2-(1,4,5,8-tetrabromo-6-hydroxy-3-oxoxanthen-9-yl)benzoic acid
- Cas Number:
- 18472-87-2
- Molecular formula:
- C20H4Br4Cl4O5.2Na
- IUPAC Name:
- 2',4',5',7'-tetrabromo-4,5,6,7-tetrachloro-3',6'-dihydroxy-3H-spiro[2-benzofuran-1,9'-xanthen]-3-one
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
- Details on test material:
- - Name of test material (as cited in study report): PHLOXINE B
- Molecular formula (if other than submission substance): C20H4Br4Cl4O5.2Na
- Molecular weight (if other than submission substance): 829.64 g/mol
- Substance type: Organic
- Physical state: Red-brown powder
- Impurities (identity and concentrations): < 5 ( weight loss on drying < 10%; chloride and sulphate < 5% )
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report):PHLOXINE B
- Molecular formula :C20H4Br4Cl4O5.2Na
- Molecular weight :829.64 g/mol
- Substance type: Organic
- Physical state: Red-brown powder
- Impurities (identity and concentrations): < 5 ( weight loss on drying < 10%; chloride and sulphate < 5% )
Test animals
- Species:
- mouse
- Strain:
- other: Jcl:ICR
- Details on species / strain selection:
- No data available
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Nippon CLEA Co., Ltd, Tokyo.
- Age at study initiation: 8-9 wk old)
- Weight at study initiation:
(P) 26--31 g- female, male - No data available.
(F1)- No data available
. - Fasting period before study: No data available.
- Housing: Males were housed singly and females four to a cage.
- Diet (e.g. ad libitum): commercial diet
(Nippon CLEA, CE-2) ad lib.
- Water (e.g. ad libitum): tap-water ad lib.
- Acclimation period: 1 week.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23 + I°C
- Humidity (%):55 + 5%
- Air changes (per hr): No data available.
- Photoperiod (hrs dark / hrs light): 12-hr light/dark cycle
IN-LIFE DATES: From: To No data available.
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: Nippon CLEA, CE-2
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: No data available
DIET PREPARATION
- Rate of preparation of diet (frequency): No data available
- Mixing appropriate amounts with (Type of food): Nippon CLEA, CE-2 commercial diet
- Storage temperature of food: No data available
VEHICLE
- Justification for use and choice of vehicle (if other than water): No data available
- Concentration in vehicle: 0, 1.0, 3.0 and 5.0%
- Amount of vehicle (if gavage): No data available
- Lot/batch no. (if required): No data available
- Purity: No data available - Details on mating procedure:
- - M/F ratio per cage:1:1
- Length of cohabitation:Overnight.
- Proof of pregnancy: [vaginal plug / sperm in vaginal smear] referred to as [day 0 / day 1] of pregnancy Females with vaginal plugs were considered to be in day 0 of pregnancy.
- After … days of unsuccessful pairing replacement of first male by another male with proven fertility.No data available
- Further matings after two unsuccessful attempts: [no / yes (explain)]No data available
- After successful mating each pregnant female was caged (how):Females were housed individually.
- Any other deviations from standard protocol:No data available - Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No data available
- Duration of treatment / exposure:
- 11 day (6-16 day of gestation)
- Frequency of treatment:
- daily
- Details on study schedule:
- Pregnant Jcl:ICR mice were given Phloxine B in the diet at concentrations of 0, 1, 3 and 5% from the morning of day 6 through day 16 of gestation. The mice were killed on day 18 and fetuses were examined for external, visceral and skeletal anomalies.
Doses / concentrations
- Remarks:
0, 1.0, 3.0 and 5.0%(2000,6000 and 10000 mg/kg/day)
- No. of animals per sex per dose:
- Total No – 84 Female
0 % (0mg/kg/day)22 females
1%(2000 mg/kg/day)21 females
3%(6000 mg/kg/day)20 females
5% (10000 mg/kg/day)21 females - Control animals:
- yes, concurrent vehicle
- Details on study design:
- No data available
- Positive control:
- No data available
Examinations
- Parental animals: Observations and examinations:
- Parental animal: observation and examination:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
- Cage side observations checked in table [No.?] were included.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule:
BODY WEIGHT: Yes
- Time schedule for examinations: Dams were weighed on days 6, 12, 16 and 18.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): yes
- 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 data
- Time schedule for examinations:
OTHER: - Oestrous cyclicity (parental animals):
- No data available
- Sperm parameters (parental animals):
- No data available
- Litter observations:
- Foetal body weight was observed
- Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: All surviving animals [describe when, e.g. as soon as possible after the last litters in each generation were produced.]
- Maternal animals: All surviving animals [describe when, e.g. after the last litter of each generation was weaned.]yes on day 18 the mice were killed under ether anaesthesia
GROSS NECROPSY
- Gross necropsy consisted of [external and internal examinations including the cervical, thoracic, and abdominal viscera.]Absolute and Relative organ weight, numbers of corpora lutea, implantations or live fetuses were observed.
HISTOPATHOLOGY / ORGAN WEIGHTS
The tissues indicated in Table [#] were prepared for microscopic examination and weighed, respectively. - Postmortem examinations (offspring):
- SACRIFICE
- The F1 offspring not selected as parental animals and all F2 offspring were sacrificed at [#?] days of age.
- These animals were subjected to postmortem examinations (macroscopic and/or microscopic examination) as follows:
GROSS NECROPSY
- Gross necropsy consisted of [external and internal examinations including the cervical, thoracic, and abdominal viscera.]Fetuses were observed for soft tissue abnormalities and skeletal anomalies.
HISTOPATHOLOGY / ORGAN WEIGTHS
The tissues indicated in Table [#] were prepared for microscopic examination and weighed, respectively. - Statistics:
- The litter was considered to be the experimental unit for the analysis of data on embryo/foetal toxicity and teratogenicity. Statistical significance of the differences between groups was determined by the Mann-Whitney U test (Siegel, 1956). Two-tailed tests were performed and P < 0.05was selected as the level of statistical significance
- Reproductive indices:
- Number of females with live fetuses, resorptions, Number of dead fetuses and total resorptions were examined.
- Offspring viability indices:
- No data available
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No overt signs of toxicity were observed in treated dams.
- Dermal irritation (if dermal study):
- not specified
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- In 10,000 mg/kgbw/day, 2 dams died on days 16 and 17. Another female in this group
aborted on day 17.These three animals were excluded from all computations. - Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Significantly decreased in Maternal body-weight gains for days 6-16 of gestation were observed in 2000, 6000 and 10,000 mg/kg bw/day treated dams as compared to control.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Average food intakes of the groups were approximately equal both in treated and control group.
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- effects observed, treatment-related
- Description (incidence and severity):
- The numbers of corpora lutea, implantations or live foetuses in all of the treated groups were slightly decreased, but not significantly in comparison with those of the control. No effect were observed on Number of dead fetuses, Total resorptions and Number of live fetuses of treated rats as compared to control.
Details on results (P0)
In 10,000 mg/kgbw/day, 2 dams died on days 16 and 17. Another female in this group
aborted on day 17.
These three animals were excluded from all computations.
Clinical signs: No overt signs of toxicity were observed in treated dams.
Body weight:
Significantly decreased in Maternal body-weight gains for days 6-16 of gestation were observed in 2000, 6000 and 10,000 mg/kg bw/day treated dams as compared to control.
Food consumption: Average food intakes of the groups were approximately equal both in treated and control group.
Test substance intake: No data available
Reproductive function: estrous cycle: No data available
Reproductive function: sperm measures: No data available
Reproductive performance: The numbers of corpora lutea, implantations or live foetuses in all of the
treated groups were slightly decreased, but not significantly in comparison with those of the control.
No effect were observed on Number of dead fetuses, Total resorptions and Number of live fetuses of treated rats as compared to control.
Gross pathology: No data available
Histopathology: No data available
Effect levels (P0)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 2 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- other: No adverse effect on survival, clinical signs, body weight, food consumption, organ weight and reproductive performance
- Remarks on result:
- other: No effects on reproductive performance
- Dose descriptor:
- LOAEL
- Effect level:
- 6 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- mortality
- body weight and weight gain
- organ weights and organ / body weight ratios
- Remarks on result:
- other: toxic effects was observed
Target system / organ toxicity (P0)
- Critical effects observed:
- not specified
- System:
- other: not specified
- Organ:
- not specified
- Treatment related:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- not specified
- Dermal irritation (if dermal study):
- not specified
- Mortality / viability:
- no mortality observed
- Description (incidence and severity):
- No effect were observed on number of live fetuses in treared rats
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Foetuses with open eyelids were observed in all treated dams. Exencephaly, significantly increased incidence of cleft palate were observed in 10,000 mg/kgbw/day treated fetuses as compaed to control. These types of external abnormalities have been seen spontaneously in this strain.
- Histopathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Significantly decreased numbers of ossified caudal vertebrae and phalanges, slightly reduced incidence of accessory sternebrae and significantly increased numbers of foetuses with a fourteenth rib or with an extra rib (at least one fourteenth rib that was half or greater than half the length of the preceding rib) were observed in 10,000 mg/kgbw/day dose group.
- Other effects:
- not specified
- Description (incidence and severity):
- Increase in fourteenth or extra ribs might be taken as an indicator of the possible teratogenic potential of a chemical.
Slight retardation of ossification were observed in 6000 mg/kgbw/day treaed fetuses as compared to control.
Splitting of the cervical vertebral arches were observed in 2000 mg/kg bw/day treatet fetouses.
Developmental neurotoxicity (F1)
- Behaviour (functional findings):
- not specified
Developmental immunotoxicity (F1)
- Developmental immunotoxicity:
- not specified
Details on results (F1)
No effect were observed on number of live fetuses in treared rats
Clinical signs: No data available
Gross pathology: Foetuses with open eyelids were observed in all treated dams.
Exencephaly, significantly increased incidence of cleft palate were observed in 10,000 mg/kgbw/day treated fetuses as compaed to control.
These types of external abnormalities have been seen spontaneously in this strain.
Histopathology: Significantly decreased numbers of ossified caudal vertebrae and phalanges, slightly reduced incidence of accessory sternebrae and significantly increased numbers of foetuses with a fourteenth rib or with an extra rib (at least one fourteenth rib that was half
or greater than half the length of the preceding rib)
were observed in 10,000 mg/kgbw/day dose group.
Increase in fourteenth or extra ribs might be taken as an indicator of the possible teratogenic potential of a chemical.
Slight retardation of ossification were observed in 6000 mg/kgbw/day treaed fetuses as compared to control.
Splitting of the cervical vertebral arches were observed in 1000 mg/kg bw/day treatet fetouses.
Effect levels (F1)
- Dose descriptor:
- LOAEL
- Generation:
- F1
- Effect level:
- 2 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Adverse effect on gross pathology and histopathology
- Remarks on result:
- other: Developmental effects was observed
Target system / organ toxicity (F1)
- Critical effects observed:
- not specified
- System:
- other: not specified
- Organ:
- not specified
- Treatment related:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
- Treatment related:
- not specified
- Relation to other toxic effects:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
Any other information on results incl. tables
Maternal and reproductive data for mice given 0-5% Phloxine B in the diet during days 6-16 of gestation
Parameters |
group |
Value in control or treated group |
|||
Control |
1% |
3% |
5% |
||
No. of pregnant females examined |
|
22 |
21 |
20 |
21 |
No. of females with live foetuses |
|
22 |
21 |
20 |
18+ |
Maternal body-wt gain (g, days 6-16) |
|
20.5 |
18.5* |
18.2* |
17.1* |
No. of corpora lutea/dam |
|
14.8 |
13.7 |
14.1 |
14.3 |
No. of implantations/dam |
|
13.9 |
12.8 |
12.4 |
13.0 |
No. of resorptions/dam |
|
1.0 |
1.4 |
0.7 |
1.1 |
No. of dead foetuses/dam |
|
0.1 |
0.1 |
0.3 |
0.2 |
Total resorptions (%) |
|
8.0 |
11.7 |
8.2 |
9.5 |
No. of live foetuses/litter |
|
12.8 |
11.3 |
11.4 |
11.8 |
Total no. of live foetuses (male/female) |
|
136/145 |
114/124 |
117/111 |
108/104 |
Mean foetal body weight (g) |
|
1.42 |
1.44 |
1.43 |
1.42 |
Maternal liver weight |
|
|
|
|
|
Absolute (g) |
|
3.04 |
2.88 |
3.12 |
3.47* |
Relative (g/100 g body wt) |
|
10.7 |
10.2 |
11.0 |
12.2 |
+One dam aborted and two dams died before day 18 of gestation. These three dams were excluded from all computations.
Values marked with asterisks are significantly different from the corresponding control value (*P < 0.05;Mann-Whitney U test).
Incidence of external and soft-tissue anomalies in foetuses of mice given 0-5% Phloxine B in the diet during days 6-16 of gestation
Anomalies |
group |
No. of foetuses (litters) affected |
|||
Control |
1% |
3% |
5% |
||
External anomalies |
|||||
No. of foetuses (litters) examined |
|
281(22) |
238(21) |
228(20) |
212(18) |
No. abnormal |
8(7) |
4(3) |
7(4) |
11(6) |
|
Open eyelids |
7(6) |
4(3) |
7(4) |
1(1) |
|
Exencephaly |
1(1)+ |
0 |
0 |
1(1) |
|
Cleft palate |
1(1) |
0 |
0 |
9(5)* |
|
Soft-tissue anomalies |
|||||
No. of foetuses (litters) examined** |
|
102(22) |
86(21) |
89(20) |
77(18) |
+ This anomaly occurred in a foetus affected with open eyelids.
**None of the foetuses examined showed any visceral anomalies.
Values marked with asterisks are significantly different from the corresponding control
Mann-Whitney U test).
Skeletal data for foetuses of mice given 0-5% Phloxine B in the diet during days 6-16 of gestation
Observation |
group |
Incidence + |
|||
|
control |
1% |
2% |
3% |
|
No. of foetuses examined |
|
179(22) |
152(21) |
139(20) |
135(18) |
No. of ossified caudal vertebrae per foetus |
9.71 |
9.39 |
9.63 |
8.25* |
|
No. of ossified phalanges in forelimbs per foetus |
10.2 |
9.74 |
10.0 |
7.85* |
|
No. of ossified phalanges in hindlimbs per foetus |
10.7 |
10.1 |
10.3 |
7.53* |
|
Accessory sternebrae |
26(11) |
16(12) |
21(12) |
9(8) |
|
Cervical rib |
18(11) |
14(8) |
25(10) |
24(12) |
|
Fourteenth rib |
67(21) |
76(18) |
68(17) |
112(18)* |
|
Extra rib** |
33(14) |
39(15) |
47(15) |
93(18)* |
|
Skeletal anomalies |
|||||
No. abnormal |
|
1(1) |
3(3) |
14(9)* |
42(14)* |
Fused ribs |
1(1) |
1(1) |
0 |
0 |
|
Fusion of the cervical vertebral arches |
0 |
0 |
0 |
2(2)+0 |
|
|
|
|
|
|
|
Fusion of the lumber vertebral bodies |
0 |
0 |
0 |
1(1) |
|
Splitting of the thoracic vertebral arche |
0 |
0 |
0 |
3(2) |
|
Splitting of the cervical vertebral arches (nos 3-6) |
|
0 |
2(2) |
14(9)* |
37(14)** |
+Where appropriate, this is given as the no. of foetuses affected and, in parentheses, the no. of litters containing affected foetuses.
*Extra rib was defined as at least one 14th rib that was half or greater than half the length of the preceding rib.
**One anomaly occurred in a foetus affected with splitting of the cervical vertebral arches
Numbers marked with asterisks are significantly different from the corresponding control number (*P < 0.05,Mann-Whitney U test on litter data
Applicant's summary and conclusion
- Conclusions:
- NOAEL was considered to be 2000 mg/kg body weight/day (1%) for F0 generation and LOAEL was considered to be 2000 mg/kg body weight/day (1%) for F1 genration when Jcl:ICR female mice treated with Phloxine B.
- Executive summary:
In a reproductive and developmental toxicity study, Jcl:ICR female mice treated with Phloxine B(18472 -87-2). 84 females mice were used in the study.The female were caged with male in pairs overnight. The next morning female with vaginal plugs were considered to be in day 0 of pregnancy and were housed individually. The test material administered in the concentration of 0, 2000,6000 and 10000 mg/kg/day (0, 1.0, 3.0 and 5.0 %)from the morning of day 6 through day 16 of pregnancy by oral feed. Animals were observed daily, beginning on day 6 of pregnancy, and were weighed on days 6, 12, 16 and 18. Food consumption and spillage were measured at regular intervals beginning on day 6 of pregnancy, and net amounts of food ingested were calculated. On day 18, the mice were killed under ether anaesthesia, and the maternal liver weight was recorded. Their reproductive status was determined. Corpora lutea were counted under a dissecting microscope. Implantation sites in each uterine horn were counted and the general condition of each conceptus was recorded. The live foetuses were removed, weighed, sexed and examined for external malformations. A third of the foetuses in each litter (selected randomly) were fixed in Bouin's solution and examined for soft-tissue abnormalities by a modified razor-section technique.The remainder were fixed in 95%ethanol, cleared with 1% KOH, stained with Alizarin Red S (Dawson, 1926) and examined for skeletal alteration.2 dams died on days 16 and 17. Another female in this group aborted on day 17.Significantly decreased in Maternal body-weight gains for days 6-16 of gestation were observed in 2000, 6000 and 10,000 mg/kg bw/day treated dams as compared to control. Similarly, the numbers of corpora lutea, implantations or live foetuses in all of the treated groups were slightly decreased, but not significantly in comparison with those of the control. Absolute and relative liver weight was significantly increased in 2000 mg/kg bw/day dose group as compared to control in F0 generation. In addition, Foetuses with open eyelids were observed in all treated dams. Exencephaly, significantly increased incidence of cleft palate and Significantly decreased numbers of ossified caudal vertebrae and phalanges, slightly reduced incidence of accessory sternebrae and significantly increased numbers of foetuses with a fourteenth rib or with an extra rib (at least one fourteenth rib that was half or greater than half the length of the preceding rib) were observed in 10,000 mg/kgbw/day treated fetuses as compared to control. Slight retardation of ossification was observed in 6000 mg/kgbw/day treated foetuses as compared to control. Splitting of the cervical vertebral arches was observed in 1000 mg/kg bw/day treated foetuses as compared to control. Hence, dose response was seen in the total incidence of skeletal abnormalities, suggested a teratogenic effect. Therefore, NOAEL was considered to be 2000 mg/kg body weight/day (1%) for F0 generation and LOAEL was considered to be 2000 mg/kg body weight/day (1%) for F1 generation when Jcl:ICR female mice were treated with Phloxine B orally by feed from day 6 to 16 of gestation.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.