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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 208-253-0 | CAS number: 518-47-8
- 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
Link to relevant study records
- Endpoint:
- one-generation reproductive toxicity
- Remarks:
- based on generations indicated in Effect levels (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data is from Peer-reviewed journal
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 421 (Reproduction / Developmental Toxicity Screening Test)
- Principles of method if other than guideline:
- Teratogenicity study of Fluorescein sodium in rabbits
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- EST ANIMALS
- Source: No data available
- Age at study initiation: (P) x wks; (F1) x wks No data available
- Weight at study initiation: (P) Males: x-x g; Females: x-x g; (F1) Males: x-x g; Females: x-x g: 4.5 kg
- Fasting period before study: No data available
- Housing: No data available
- Diet (e.g. ad libitum): No data available
- Water (e.g. ad libitum): No data available
- Acclimation period: No data available
ENVIRONMENTAL CONDITIONS
- Temperature (°C): No data available
- Humidity (%):No data available
- Air changes (per hr): No data available
- Photoperiod (hrs dark / hrs light): No data available - Route of administration:
- intravenous
- Type of inhalation exposure (if applicable):
- not specified
- Vehicle:
- other: 10% water solution (Funduscein)
- Details on mating procedure:
- - M/F ratio per cage: No data available
- Length of cohabitation: No data available
- Proof of pregnancy: [vaginal plug / sperm in vaginal smear] referred to as [day 0 / day 1] of pregnancy No data available
- 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): No data available
- Any other deviations from standard protocol: Nineteen rabbits immediately after copulation with male rabbits of the same species were used. - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 3 days (5,6 and 8 day after copulation)
- Frequency of treatment:
- Once daily on 5,6 and 8 day after copulation
- Details on study schedule:
- No data available
- Remarks:
- Doses / Concentrations:
1.4 ml (2241.4 mg/kg)
Basis:
actual ingested - No. of animals per sex per dose:
- Total: 19
0 ml: 4 female
2241.4 mg/kg: 15 female - Control animals:
- yes, concurrent vehicle
- Details on study design:
- No data available
- Positive control:
- No data available
- Parental animals: Observations and examinations:
- Survival and clinical sign were examined.
- Oestrous cyclicity (parental animals):
- Any irriggularty in Estrous cyclicity were examined.
- Sperm parameters (parental animals):
- No data available
- Litter observations:
- Delayed appearance of birth defects were examined.
- Postmortem examinations (parental animals):
- No data available
- Postmortem examinations (offspring):
- Gross pathology and histopathology were examined.
- Statistics:
- The difference between the number of offspring that died at one month in the experimental vs the control group was analyzed with the Chi-square test. The probability that the distribution occurred by chance was found to be at the 5% level of significance (P = .05).
- Reproductive indices:
- No data available
- Offspring viability indices:
- Viability till four weeks were observed
- Clinical signs:
- no effects observed
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Other effects:
- not specified
- Reproductive function: oestrous cycle:
- not specified
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- no effects observed
- Dose descriptor:
- NOAEL
- Effect level:
- 2 241.4 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- other: No effect on survival, clinical sign and Reproductive performance
- Clinical signs:
- no effects observed
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- not specified
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- no effects observed
- Histopathological findings:
- no effects observed
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 2 241.4 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No effect on survival, clinical sign, Gross pathology and histopathology
- Reproductive effects observed:
- not specified
- Conclusions:
- NOAEL was considered to be 2241.4 mg/kg when New Zealand female Rabbits were treated with Fluorescein sodium.
- Executive summary:
In a Teratogenicity study,New Zealand female Rabbits were treated with Fluorescein sodium in the concentration of 2241.4 mg/kg intravenouslly in 10% water solution (Funduscein) on day 5,6 and 8 day after copulation. No effect was observed on survival and no abortion or miscarriages were observed in treated rats as compared to control. No effect on live-born offspring and stillbirth were observed in treated rabbits as compared to control. No effect on live-born offspring was observed. At 4 week, 14 offspring (19%) from four mothers subsequently died. The observed effects were due to poor mothers and not due to treatment. One stillbirth and all other offspring were normal and no delayed appearances of birth defects were observed in offspring as compared to control. In addition, no gross pathological and histopathological changes were observed in offspring of treated rabbits as compared to control. Therefore, NOAEL was considered to be 2241.4 mg/kg for F0 and F1 generation when New Zealand female Rabbits were treated with Fluorescein sodium intravenouslly in 10% water solution (Funduscein) on day 5, 6 and 8 day and day 13, 15 and 16 day after copulation.
Reference
Clinical signs:
No abortion or miscarriage were observed in trated rats as compared to control.
Body weight and food consumption: No data available
Test substance intake: No data available
Reproductive function: estrous cycle: No data available
Reproductive function: sperm measures: No data available
Reproductive performance:No effect on live-born offspring and stillbirth were observed in treated rats as compared to control.
Organ weights No data available
Gross pathology: No data available
Histopathology: No data available
other findings No data available
No effect on live-born offspring were observed in trated rats as compared to control.
At 4 week, 14 offspring (19%) from four mothers subsequently died.
The observed effect were due to poor mothers not due to treatment.
Clinical signs:
One stillbirth and all other offspring were normal and no delayed appearance of birth defects were observed in offspring as compared to control.
Body weight and food consumption: No data available
Test substance intake: No data available
Reproductive function: estrous cycle: No data available
Reproductive function: sperm measures: No data available
Reproductive performance: No data available
Organ weights: No data available
Gross pathology:No gross pathological changes were observed in offspring of treated rats.
Histopathology:No Soft tissue and Visceral abmormalities were observed in offspring of treated rats.
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 2 241.4 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rabbit
- Quality of whole database:
- Data is Klimish 2 and from peer reviewed journal
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Reproductive toxicity:
Data available for target Sodium fluorescein (CAS no 5185-47-8) for reproductive toxicity are summarized as below.
In a study conducted by Mcenerneyet al(1977), Teratogenicity was evaluated in New Zealand female Rabbits treated with Fluorescein sodium in the concentration of 2241.4 mg/kg intravenouslly in 10% water solution (Funduscein) on day 5, 6 and 8 and day 13, 15 and 16 after copulation. No effect was observed on survival and no abortion or miscarriages were observed in treated rats as compared to control. No effect on live-born offspring and stillbirth were observed in treated rabbits as compared to control. No effect on live-born offspring was observed. At 4 week, 14 offspring (19%) from four mothers subsequently died. The observed effects were due to poor mothers and not due to treatment. One stillbirth and all other offspring were normal and no delayed appearances of birth defects were observed in offspring as compared to control. In addition, no gross pathological and histopathological changes were observed in offspring of treated rabbits as compared to control. Therefore, NOAEL was considered to be 2241.4 mg/kg for F0 and F1 generation when New Zealand female Rabbits were treated with Fluorescein sodium intravenouslly in 10% water solution (Funduscein) on day 5, 6 and 8 day and day 13, 15 and 16 day after copulation.
In a study conducted by Burnetiet al(1986), Teratogenic toxicity was evaluated in Dutch Belted female Rabbits treated with D&C Yellow no 8 in the concentration of 0, 30, 100 and 250 mg/kg body weight/day by oral gavage. One rabbits died each in 30 and 250 mg/kg bw/day including control. One rabbit aborted on day 28 of gestation at 250 mg/kg bw/day as compared to control. Pneumonia was observed in three rabbit which were died. Orange discoloration of the urine was observed in all the treated rabbits between days 7 and 28 of gestation as compared to control. No effect on body weight and body weight gain and No effect on Post-implantation loss/dam, Total implantations/dam and Corpora lutea/dam were observed in treated rabbits as compared to control. Similarly, There were no biologically meaningful or statistically significant differences in the number of litters, Foetal sex and gross pathological changes were observed in treated rabbits as compared to control. In addition, No effect on viability of foetus, foetal body weight and sex of foetus were observed as compared to control. At 30 and 100 mg/kg be/day, malformations were observed in two foetuses from two litters. However, these values fell within the ranges of historical control data. There were no biologically meaningful or statistically significant differences in number of fetuses with malformations, number of foetuses or litters with developmental variations were observed in foetuses of any of the treated groups. Therefore, NOAEL was considered to be 250 mg/kg body weight /day for F0 and F1 generation when Dutch Belted female rabbits were treated with D&C Yellow no 8 orally by gavage from day 6 to 27 of gestation.
In a above similar reference, Teratogenic toxicity was evaluated in CD Sprague-Dawley female rats treated with D&C Yellow no. 8 in the concentration of 0, 100, 500 and 1500 mg/kg body weight/day by oral gavage. Six rats died during the dosing period and at 1500 mg/kg bw/day and Orange discoloration of the urine was observed in all the treated rats as compared to control. Similarly, green discoloration of the amniotic fluid and green colored small intestines were observed at 1500 mg/kg bw/day and green discoloration of the amniotic fluid was observed at 100 and 500 mg/kg bw/day treated rats as compared to control. No effect on Post-implantation loss/dam, Total implantations/dam, Corpora lutea/dam and There were no biologically meaningful or statistically significant differences in the number of litters and Foetal sex of treated rats were observed as compared to control. In addition, No effect on viability of foetuse, number of fetuses with malformations, number of foetuses or litters with developmental variations were observed in any of the treated groups. Slight increase in the number of litters with unossified sternebrae (sternebrae nos 1-6) and rudimentary 14thrib(s) was observed in feotus of 1500 mg/kg bw/day treated rats as compared to control, but the observed effect fell within the ranges of historical control data. Therefore, NOAEL was considered to be 1500 mg/kg body weight /day for F0 and F1 generation when CD Sprague-Dawley female rats were treated with D&C Yellow no. 8 orally by gavage for 14 days.
Thus, based on the above available data for target sodium fluorescein (CAS no 518-47-8) from peer reviewed journals is not likely to be classified as a reproductive toxicant in rabbits and rats.
Short description of key information:
NOAEL was considered to be 2241.4 mg/kg for F0 and F1 generation when New Zealand female Rabbits were treated with Fluorescein sodium
Justification for selection of Effect on fertility via oral route:
NOAEL was considered to be 2241.4 mg/kg for F0 and F1 generation when New Zealand female Rabbits were treated with Fluorescein sodium intravenouslly in 10% water solution (Funduscein) on day 5, 6 and 8 day and day 13, 15 and 16 day after copulation.
Effects on developmental toxicity
Description of key information
NOAEL was considered to be 1500 mg/kg bw F0 and F1 generation when Sprague-Dawley Female rats were treated with D & C Yellow No. 8
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data is from peer- reivewed journal
- Principles of method if other than guideline:
- The teratogenic potential was determined in Sprague dawley rats after the administration of D & C Yellow No. 8 by gavage
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Portage, Michigan
- Age at study initiation: 14 weeks
- Weight at study initiation:No data available
- Fasting period before study:No data available
- Housing:No data available
- Diet (e.g. ad libitum):No data available
- Water (e.g. ad libitum):No data available
- Acclimation period: 4 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 72 ± 4F
- Humidity (%): 50 ± 15%
- Air changes (per hr): No data avaialble
- Photoperiod (hrs dark / hrs light): 2-hrlight/dark cycle
IN-LIFE DATES: From: To:No data available - Route of administration:
- oral: gavage
- Type of inhalation exposure (if applicable):
- not specified
- Vehicle:
- not specified
- Details on exposure:
- From day 6-19 days of gestation
- Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- - M/F ratio per cage: No data available
- Length of cohabitation: No data available
- Proof of pregnancy: [vaginal plug / sperm in vaginal smear] referred to as [day 0 / day 1] of pregnancy Copulatory plug or presence of sperm in vaginal washings.
- 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
- After successful mating each pregnant female was caged (how): They were housed individually and offered Purina Certified Rodent Chow No. 5002 and water ad lib.
- Any other deviations from standard protocol: Not mentioned - Duration of treatment / exposure:
- 14 days
- Frequency of treatment:
- Daily
- Duration of test:
- days 6-19 of gestation
- No. of animals per sex per dose:
- Total: 100
0 mg/Kg bw: 25
100 mg/Kg bw: 25
500 mg/Kg bw: 25
1500 mg/Kg bw: 25 - Control animals:
- yes, concurrent vehicle
- Maternal examinations:
- Caesarean sections were performed on all surviving females killed with carbon dioxide on gestation day 20 The number and location of viable and non-viable foetuses, early and late resorptions, total implantations and corpora lutea were recorded.
- Ovaries and uterine content:
- Gravid and Nongravid uteri were examined.
- Fetal examinations:
- Foetal sex ratio, foetal body weight, gross pathology and histopathology were examined.
- Statistics:
- Differences in the Ibctal scx distribution and the number of litters with malformations between control and treated groups wcre compared using the Chi-square test criterion with Yates" correction for 2 x 2 contingency lables and, or Fisher's exact probability test as described by Sicgel (1956). The numbers of early and late resorptions, dead foetuses and post-implantation losses were compared between groups by the Mann Whitney U test as described by Siegel (1956) and Well (1970). The mean numbers of viable foetuses, total implantations, corpora lutca and mean t\)etal weights were compared between groups by analysis of variance (oneway classification), Bartlett's test l\~r homogeneity of variances, and the appropriate t test (for equal or unequal variances) as described by Steel & Torric (1960) using Dunnctt's multiple comparison tables (1964).
- Indices:
- Dams with viable foetuses, Viable foetuses/dam, Post-implantation loss, Total implantations and Corpora lutea were examined.
- Historical control data:
- No data available
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Mortality:
when treated wtih 1500 mg/kg bw, Six rats died as compared to control.
Clinical sign:
Orange discoloration of the urine was observed in 100, 500 and 1500 mg/kg bw treated rats.
Body weigth gain:
Slight decrease in body weight gain were observed in 1500 mg/kg bw treated rats as compared to control.
Reproductive indices:
No effect on dams with viable foetuses, viable foetuses/dam, post-implantation loss, total implantations, corpora lutea and number of litters with malformations were examined.
Gross pathology:
Green discoloration of the amniotic fluid was observed in 1, 10 and 16 rats in the 100, 500 and 1500 mg/kg/day treated rats as compared to control. - Dose descriptor:
- NOAEL
- Effect level:
- 1 500 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No significant effect on Foetal sex ratio, foetal body weight, gross pathology and histopathology were observed. - Dose descriptor:
- NOAEL
- Effect level:
- 1 500 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No effect on foetal body weight, sex retio, gross pathology and histopathology
- Abnormalities:
- not specified
- Developmental effects observed:
- not specified
- Conclusions:
- NOAEL was considered to be 1500 mg/kg bw when Sprague-Dawley Female rats were treated with D & C Yellow No. 8 orally by gavage from day 6-19 of gestation.
- Executive summary:
In a teratogenic potential study, Sprague-Dawley Female rats were treatedw with D & C Yellow No. 8 in the concentration of 0, 100, 500 and 1500mg/kg body weight orally by gavage. Six rats died at 1500 mg/kg bw as compared to control. Orange discoloration of the urine was observed in 100, 500 and 1500 mg/kg bw treated rats and Slight decrease in body weight gain were observed in 1500 mg/kg bw treated rats as compared to control. Green discoloration of the amniotic fluid was observed in 1, 10 and 16 rats in the 100, 500 and 1500 mg/kg/day treated rats as compared to control. But, no effect on dams with viable foetuses, viable foetuses/dam, post-implantation loss, total implantations, corpora lutea and number of litters with malformations were examined in treated rats as compared to control. In addition, No significant effect on Foetal sex ratio, foetal body weight, gross pathology and histopathology were observed. Therefore, NOAEL was considered to be 1500 mg/kg bw when Sprague-Dawley Female rats were treated with D & C Yellow No. 8 orally by gavage from day 6-19 of gestation.
Based on the observations these doses did not result in evidence of maternal toxicity or adverse effects on foetal development.
Reference
Mean maternal body weights changesfor rats given D & (" Yellow No. 8 by gavage on days 6 -19 of gestation
Day of gestation |
No. of foetuses (no. of litters) |
|||
|
0 |
100mg/kg |
500mg/kg |
1500mg/kg |
0 |
246±145 |
249 ± I3.7 |
5249±14.7 |
241±12. 4 |
6 |
272±16.8 |
271 ± 14.4 |
276±14.5 |
263 ± 12.2 |
9 |
279±18,1 |
278 ± 15.9 |
283±16.7 |
269 ±16.5 |
12 |
294±20.1 |
292 ± 17.5 |
296 ± 16.1 |
282 ±16.9 |
16 |
321±23.4 |
320 ± 18.9 |
323 ± 20.4 |
300 ± 30.7 |
20 |
379±30.0 |
378 ±21.2 |
374 ±32.2 |
359 ±33.3 |
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 500 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Data is Klimish 2 and from peer reviewed journal
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Developmental toxicity:
Data available for target Sodium fluorescein (CAS no 5185-47-8) for developmental toxicity are summarized as below.
In a study conducted by Burnetiet al(1986), teratogenic potential was evaluated in Sprague-Dawley Female rats by using D & C Yellow No. 8 in the concentration of 0, 100, 500 and 1500mg/kg body weight orally by gavage. Six rats died at 1500 mg/kg bw as compared to control. Orange discoloration of the urine was observed in 100, 500 and 1500 mg/kg bw treated rats and Slight decrease in body weight gain were observed in 1500 mg/kg bw treated rats as compared to control. Green discoloration of the amniotic fluid was observed in 1, 10 and 16 rats in the 100, 500 and 1500 mg/kg/day treated rats as compared to control. But, no effect on dams with viable foetuses, viable foetuses/dam, post-implantation loss, total implantations, corpora lutea and number of litters with malformations were examined in treated rats as compared to control. In addition, No significant effect on Foetal sex ratio, foetal body weight, gross pathology and histopathology were observed. Therefore, NOAEL was considered to be 1500 mg/kg bw F0 and F1 generation when Sprague-Dawley Female rats were treated with D & C Yellow No. 8 orally by gavage from day 6-19 of gestation.
In a above similar study, teratogenic potential was evaluated in Dutch Belted Female rabbits by using D & C Yellow No. 8 in the concentration of 0, 30, 100 and 250 mg/kg body weight orally by gavage. One rabbit died in 30, 25 and in control due to pneumonia and one rabbit aborted on day 28 of gestation in 250 mg/kg bw. Green discoloration of the urine was observed in 30, 100 and 250 mg/kg bw treated rabbits. No effect on body-weight gains were observed in treated rabbits. Similarly, No statistically significant effect on numbers of corpora lutea, total implantations and early or late resorptions were observed in treated rabbits as compared to control. In addition, No statistically significant effect on viable foetuses, foetal sex, distribution or mean foetal body weight, external, visceral and skeletal foetal malformations and developmental variations were observed in treated rabbits. Only malformations observed occurred in two foetuses from two litters in both the 30 and 100 mg/kg/day groups and these have been observed in historical control data. Therefore, NOAEL was considered to be 250 mg/kg bw for F0 and F1 generation when Dutch Belted Female rabbits were treated with D & C Yellow No. 8 orally by gavage from day 6-27 of gestation.
In a study conducted by Salemet al(1979), Teratogenicity was evaluated in CD female rats by using sodium fluorescein in the concentration of 0 and 10000 mg/kg (10 %) by intravenous injections under light ether anesthesia into the saphenous vein on days 1, 6, 12 and 18 of pregnancy (4 different female rats per day). No statistically significant effect on number of pups per litter was observed as compared to control. In addition, No statistically significant effect on overt abnormalities, average length (cm) or weight (g) of the pups and gross external and internal organs of pups of treated rats as compared to control. Therefore, NOAEL was considered to be 10000 mg/kg for F0 and F1 generation when CD female rats were treated with sodium fluorescein intravenously into the saphenous vein on days 1, 6, 12 and 18 of pregnancy (4 different female rats per day).
In a study conducted by Mcenerneyet al(1977), Teratogenicity was evaluated in New Zealand female Rabbits treated with Fluorescein sodium in the concentration of 2241.4 mg/kg intravenouslly in 10% water solution (Funduscein) on day 5, 6 and 8 and day 13, 15 and 16 after copulation. No effect was observed on survival and no abortion or miscarriages were observed in treated rats as compared to control. No effect on live-born offspring and stillbirth were observed in treated rabbits as compared to control. No effect on live-born offspring was observed. At 4 week, 14 offspring (19%) from four mothers subsequently died. The observed effects were due to poor mothers and not due to treatment. One stillbirth and all other offspring were normal and no delayed appearances of birth defects were observed in offspring as compared to control. In addition, no gross pathological and histopathological changes were observed in offspring of treated rabbits as compared to control. Therefore, NOAEL was considered to be 2241.4 mg/kg for F0 and F1 generation when New Zealand female Rabbits were treated with Fluorescein sodium intravenouslly in 10% water solution (Funduscein) on day 5, 6 and 8 day and day 13, 15 and 16 day after copulation.
Thus, based on above available data for target sodium fluorescein (CAS no 518-47-8) from peer reviewed journals is not likely to be classified as a developmental toxicant in rabbits and rats.
Justification for selection of Effect on developmental toxicity: via oral route:
NOAEL was considered to be 1500 mg/kg bw F0 and F1 generation when Sprague-Dawley Female rats were treated with D & C Yellow No. 8 orally by gavage from day 6-19 of gestation.
Justification for classification or non-classification
sodium fluorescein (CAS no 518-47-8) from peer reviewed journals is not likely to be classified as a reproductive and developmenal toxicant in rabbits and rats.
Additional information
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.