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Administrative data

Description of key information

Oral repeated dose toxicity:

An OECD guideline Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test was performed with the Source Substance C.I. Pigment Orange 43.

 

The test item was administered to the main groups (10 male and 10 female) by oral gavage at dose levels of 0, 100, 300 and 1000 mg/kg Bwt/day. Recovery groups (5 male and 5 females) received dose levels of 0, and 1000 mg/kg Bwt/day. The dose formulations were administered prior to mating, during mating and post-mating periods for males, and prior to mating, during mating, during pregnancy and up to Lactation Day 13 for females. In the control and high dose recovery groups, the treatment period was followed by a 14 day no treatment (recovery) period. Animals in the recovery groups were not mated.

 

No toxicologically significant changes were noted in any of the parameters investigated in this study (such as clinical signs, functional observations, body weight, food consumption, clinical laboratory investigations, macroscopic examination, organ weights, and microscopic examination). A No Observed Adverse Effect Level (NOAEL) for the test item for repeated dose toxicity of 1000 mg/kg/day was established.

Key value for chemical safety assessment

Repeated dose toxicity: via oral route - systemic effects

Link to relevant study records

Referenceopen allclose all

Endpoint:
short-term repeated dose toxicity: oral
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Reason / purpose for cross-reference:
reference to same study
Qualifier:
according to guideline
Guideline:
OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
Deviations:
no
GLP compliance:
yes
Limit test:
no
Species:
rat
Strain:
Wistar
Details on species / strain selection:
HsdHan: WIST rats
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Department of Safety Assessment, Advinus Therapeutics Limited, Bengaluru 560 058, India
- Age at study initiation: 14-15 weeks

- Weight at study initiation: Males: 368 to 477 g, Females: 224 to 268 g

G1 (m/f): 424.69 ± 36.43 / 249.78 ± 12.87 g
G2 (m/f): 426.05 ± 35.33 / 256.37 ± 07.83 g
G3 (m/f): 426.61 ± 30.16 / 254.46 ± 09.92 g
G4 (m/f): 426.05 ± 28.00 / 255.30 ± 09.74 g

G1R (m/f): 407.82 ± 21.48 / 249.51 ± 05.16 g
G4R (m/f): 408.20 ± 15.55 / 247.96 ± 11.19 g

- Fasting period before study: non
- Housing: During mating, one male and one female were housed in standard polysulfone cages with stainless steel top grill. having facilities for pelleted food. Mated pairs were separated. Males were housed with their former cage mates while females were housed individually in polysulfone cages. During the study period, animals were housed in a single experimental room of T4 Barrier Area.

- Diet (e.g. ad libitum): Teklad Certified (2014C) Global 14 % Protein Rodent Maintenance Diet - Pellet manufactured by Harlan Laboratories (Envigo), P.O. Box 44220, Madison, Wi 53744-4420 was provided ad libitum to the animals.
- Water (e.g. ad libitum): Deep bore-well water passed through activated charcoal filter and exposed to UV rays was provided ad libitum to rats in polycarbonate bottles with stainless steel sipper tubes.
- Acclimation period: five days before start

DETAILS OF FOOD AND WATER QUALITY:

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21-23
- Humidity (%): 65-67
- Air changes (per hr): 12-15
- Photoperiod (hrs dark / hrs light): 12/12
Route of administration:
oral: gavage
Vehicle:
other: 0.5 % (w/v) Na CMC (medium viscosity) in Milli-Q® water
Details on oral exposure:
PREPARATION OF DOSING SOLUTIONS:
The dose formulations were prepared daily prior to start of the treatment or prepared on need basis and used within the stability period.
Homogeneity of the dose formulations during sampling/gavaging was maintained by constant stirring using a magnetic stirrer.

VEHICLE:
- Justification for use and choice of vehicle (if other than water): Based on the solubility and suspensibility test.
- Concentration in vehicle: 0 / 10 / 30 / 100 mg//mL
- Amount of vehicle (if gavage): 10 mL/kg Bwt/day

Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
For homogeneity and concentration analysis, samples were sampled in duplicate on Day 1 and once during Week 4 of the treatment and analysed. For each set, duplicate samples were drawn from top, middle and bottom layers of each preparation and in case of control, duplicate samples from only middle layer was drawn.

The analysis was done as per the method validated. One set of samples were analyzed for concentration analysis and other set (second set) of samples were stored at ambient conditions for re-analysis purpose as a backup.

Formulations were considered acceptable as mean results are within ± 15% of the theoretical concentration and the relative standard deviation (RSD) was less than 10 %.
Duration of treatment / exposure:
Males: The dose formulation was administered at least for 28 days to the rats of the specific groups once daily at approximately the same time each day (varying by ± 3 hours) for 2 weeks prior to mating and the treatment was continued during the mating period and until sacrifice.

Females: The dose formulations were administered to the specific group of rats once daily at approximately the same time each day (varying by ± 3 hours) throughout the treatment period. Treatment was done 2 weeks prior to the mating period and continued through mating, pregnancy and up to LD 13, after which, pups were sacrificed on LD 13 and parental females (dams) were sacrificed on LD 14 after overnight fasting (water allowed).

The dose formulations were administered to the high dose recovery group of rats once daily at approximately the same time each day (varying by ± 3 hours).
The volume of dose administered was 10 mL/kg Bwt/day throughout the study. The dose volume was adjusted based on the most recent body weight of individual rat.

Similarly, vehicle was administered to rats in the vehicle control and vehicle control recovery groups at 10 mL/kg Bwt/day.

The vehicle and the test item was not administered for vehicle control recovery and high dose recovery groups, respectively for 14 days following the treatment period.
Dose / conc.:
0 mg/kg bw/day (nominal)
Remarks:
G1 Vehicle Control
Dose / conc.:
100 mg/kg bw/day (nominal)
Remarks:
G2 Low dose
Dose / conc.:
300 mg/kg bw/day (nominal)
Remarks:
G3 Mid dose
Dose / conc.:
1 000 mg/kg bw/day (nominal)
Remarks:
G4 High dose
Dose / conc.:
0 mg/kg bw/day (nominal)
Remarks:
G1R Vehicle Control recovery
Dose / conc.:
1 000 mg/kg bw/day (nominal)
Remarks:
G4R High dose recovery
No. of animals per sex per dose:
10 Males and 10 Females for each main groups. 5 Males and 5 Females for each recovery group.
Control animals:
yes
Details on study design:
- Dose selection rationale: Dose levels were selected in order to induce toxic effects at the highest dose, any dosage related response and no adverse effects at the mid and lowest dose.
- Grouping: Grouping was done by the method of body weight stratification and distribution.
- Rationale for selecting satellite groups: Satellit groups were were used in the control and the top dose group for observation of reversibility, persistence or delayed occurrence of systemic toxic effects.
- Post-exposure recovery period in satellite groups: 14 day no treatment period
Positive control:
non
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS:
All rats were observed for morbidity and mortalities twice daily i.e., once in the morning and once in the afternoon. As there were no clinical signs, the observation for morbidity and mortality was carried out once in the morning during holidays. All rats were observed for clinical signs once daily during the treatment and recovery periods.

DETAILED CLINICAL OBSERVATIONS:
Detailed clinical examination was done prior to the treatment on Day 1 and at weekly intervals thereafter during treatment and recovery periods.
During detailed clinical examination, all rats were observed for changes in skin, fur, eyes, mucous membranes, occurrence of secretions and excretions and autonomic activity (e.g. lacrimation, piloerection, pupil size, unusual respiratory pattern), changes in gait, posture and response to handling as well as the presence of clonic or tonic movements, stereotypies (e.g., excessive grooming, repetitive circling or bizarre behaviour like self-mutilation and walking backwards.
On the days of detailed clinical examination, general clinical signs were not performed except on treatment Day 1

BODY WEIGHT:
i) Individual body weights of males were recorded initially and at weekly intervals thereafter. Individual body weights of females were recorded initially and at weekly intervals thereafter till cohabitation (till mating confirmation) with males.
ii) All dams were weighed on GD 0, 7, 14 and 20 and on LD 0, 4 and 13.

FOOD CONSUMPTION AND COMPOUND INTAKE:
Cagewise food consumption was calculated by using the food consumed at weekly interval per cage and dividing by the number of rats per cage and the number of days in the intervening period to determine the food intake/rat/day.
Food consumption was not measured during the cohabitation period.
Food consumption of pregnant dams was recorded on GD 7, 14 and 20 and on Day 4 and 13 of lactation period.

ESTROUS CYCLICITY:
Vaginal smear was examined and the stage of oestrous cycle was recorded daily for two weeks before start of the treatment to select for the study females with regular 4-5 days cyclicity. The vaginal smear was also examined daily from the beginning of the treatment period until evidence of mating period to determine the Day 0 of pregnancy/treatment-related effects on mating or pre-coital time. The time interval (in days) from the diestrus of an oestrous cycle to the next diestrus was considered as the oestrous cycle length of an animal. The overall pattern of each female was characterized as regular cycling (having recurring 4–5 day cycles) and irregularly cycling (having cycles with a period of diestrus longer than 3 days or a period of estrus more or less than 2 days). Incomplete cycles (having prolonged periods of either estrus or diestrus) were not included in calculating the mean cycle length.
Vaginal smears were also examined on the day of necropsy to determine the stage of the oestrous cycle.
Sacrifice and pathology:
The animals were subjected to detailed necropsy at sacrifice after overnight fasting (water allowed) and study plan specified tissues were collected. Tissues/organs collected from randomly selected 5 males and 5 females in the control and high dose groups (including reproductive organs) were examined microscopically for histopathological changes. Histopathological examination of testes also included a qualitative assessment of stages of spermatogenesis and interstitial testicular cell structure. The thyroid gland was collected from all pups on LD 13 and examined microscopically. All gross lesions were examined from all the groups.
Statistics:
ProvantisTM: Parameters of laboratory Investigations - Haematology (Coagulation tests PT and APTT data was entered retrospectively in ProvantisTM) and Clinical Chemistry data was analysed using Provantis built-in statistical tests.

The statistical analysis of the experimental data was carried out using the validated package in Excel and also using licensed copies of SYSTAT Statistical package ver.12.0. All quantitative variables like neurological observations (neuromuscular observation/body temperature/body weights), body weight, food consumption, oestrous cycle length, hormone levels, anogenital distance, organ weights and organ weight ratios were tested for normality (Shapiro-Wilk test) and homogeneity of variances (Levene’s test) within the group before performing a one-factor analysis of variance (ANOVA) modeling by treatment groups. Non-optimal (non-normal or heteroschedastic) data was transformed, before ANOVA was performed. Comparison of means between treatment groups and cont ol group was done using Dunnett’s test when the overall treatment, ‘F’ test is found to be significant.

Post-implantation loss (%), number of nipples/areolae in male pups, no. of implantations, pre-coital interval, mean litter size, sex ratio and gestation length (Days) was analysed after suitable transformation (√ x + ½) of the data. Oneway ANOVA was carried out for the transformed data. Dunnett’s pair-wise comparison of the treated means with the control mean was done when the group differences are found significant.

Z test was performed for testing the differences in proportions for mating and fertility indices.

Clinical signs:
no effects observed
Description (incidence and severity):
The orange coloured fecal pellets observed were due to the physical appearance of the test item, not related to the toxicity.
Mortality:
no mortality observed
Body weight and weight changes:
no effects observed
Food consumption and compound intake (if feeding study):
no effects observed
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
no effects observed
Description (incidence and severity):
eye examination: normal
Haematological findings:
no effects observed
Clinical biochemistry findings:
no effects observed
Urinalysis findings:
no effects observed
Behaviour (functional findings):
no effects observed
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Gross pathological findings:
no effects observed
Neuropathological findings:
no effects observed
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Microscopically, pigmented macrophages were observed in lungs at 1000 mg/kg Bwt/day in both sexes and considered as test item-related non-adverse finding. This change showed complete recovery at the end of recovery period.
Histopathological findings: neoplastic:
not specified
Other effects:
not specified
Key result
Dose descriptor:
NOAEL
Effect level:
>= 1 000 mg/kg bw/day (nominal)
Based on:
act. ingr.
Sex:
male/female
Basis for effect level:
other: highest dose applied
Key result
Critical effects observed:
no
Conclusions:
Daily oral (gavage) administration of Pigment Orange 43 to male and female Wistar rats at the dose levels of 100, 300 and 1000 mg/kg Bwt/day for 2 weeks prior to mating, during mating, and 2 weeks post mating (males) or 2 weeks prior to mating, during mating, and during pregnancy until 13 days after delivery did not induce any adverse effects.

The No Observed Adverse Effect Level (NOAEL) of Pigment Orange 43 for general toxicity (repeated dose toxicity) in males and females is considered to be 1000 mg/kg Bwt/day.

Therefore, the test item has not to be classified as subacutely toxic (STOT RD) by the oral route according to Regulation (EC) No 1272/2008.
Executive summary:

The purpose of this Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test in Wistar Rats was to determine the possible health hazards likely to arise from repeated exposure over a relatively limited period of time. Further, this study was used to provide initial information on possible effects on male and female reproductive performance such as gonadal function, mating behaviour, conception, development of the conceptus and parturition.

The test item Hostaperm-Orange GR was suspended in vehicle {0.5 % (w/v) Na CMC in Milli-Q® water} and administered by oral gavage at the dose levels of 100, 300 and 1000 mg/kg Bwt/day to low (G2), mid (G3) and high dose (G4)/ high dose recovery (G4R) group rats, respectively. A concurrent vehicle control (G1) and a vehicle control recovery group (G1R) of rats received the vehicle alone. The dose volume administered was 10 mL/kg Bwt/day. The main groups i.e., G1 to G4 consisted of 10 male and 10 female rats per group and recovery groups consisted of 5 male and 5 female rats per group. The dose formulations were administered once daily to specific group of rats prior to mating, during mating and post-mating periods (for males), during pregnancy and up to Lactation Day (LD) 13 (for females). In the control and high dose recovery groups, the treatment period was followed by a 14 day no treatment (recovery) period. The recovery period of the study was started from the first scheduled kill of dams. Animals in the recovery groups were not mated and consequently not used for assessment of reproduction/developmental toxicity.

The identity of Hostaperm-Orange GR was provided by the study Sponsor by a Certificate of Analysis (CoA). The stability and homogeneity of test item in the vehicle was carried out under Advinus Study No.G11233. Based on the results, the test item was found to be stable for up to 8 days at 1 and 100 mg/mL concentrations, when stored at room temperature. The dose formulations were analysed for active ingredient (a.i.) concentration on Day 1 and during Week 4 of the treatment period. The results indicated that the analysed concentrations were within ± 15 % of variations from the nominal concentrations.

All rats were observed for clinical signs once daily. Body weight was recorded at the beginning of the treatment, weekly thereafter and at termination. Food consumption was recorded weekly except during the cohabitation period. Female rats were also weighed on Gestation Day (GD) 0, 7, 14 and 20 and on Lactation Day (LD) 0, 4 and 13. Food consumption was recorded on GD 7, 14 and 20 and on LD 4 and 13. The number, weight, survival and mortality of pups were observed during the lactation period. The ano-genital distance of each pup was measured on LD 0. All the survived male pups were examined for the appearance nipples/areolae on post-natal day (PND) 13. The functional observation battery was done shortly before sacrifice for randomly selected 5 males and 5 females from each group. For recovery groups, functional observation battery was done towards the end of recovery period. Laboratory investigations such as hematology, coagulation, clinical chemistry and urinalysis were performed in randomly selected 5 males and 5 females from each group at the end of the pre-mating period for main groups and at the end of recovery period from all animals of recovery groups. Thyroxine 4 (T4) and Thyroid Stimulating Hormone (TSH) analysis were performed in all males at termination, all dams at termination on LD 13 and two pups per litter on LD 4 and 13. The animals were subjected to detailed necropsy at sacrifice after overnight fasting (water allowed) and study plan specified tissues were collected. Tissues/organs collected from randomly selected 5 males and 5 females in the control and high dose groups (including reproductive organs) were examined microscopically for histopathological changes. Histopathological examination of testes also included a qualitative assessment of stages of spermatogenesis and interstitial testicular cell structure. The thyroid gland was collected from all pups on LD 13 and examined microscopically. All gross lesions were examined from all the groups.

Under the experimental conditions employed, the following results were obtained:

  • There were no treatment-related clinical signs or mortality observed at any of the doses tested.
  • No treatment-related neurological abnormalities/dysfunctions were observed at all the doses tested.
  • The body weights and food consumption were unaffected by the treatment at all the doses tested.
  • The maternal body weight and food consumption during gestation and lactation periods were unaffected by the treatment at all the doses.
  • Treatment had no effect on pre-coital time or gestation length, oestrous cycle length at all the tested doses
  • No treatment-related changes were observed in the fertility indices of sires and dams at all the doses tested.
  • The survival indices were not altered by the treatment at all the doses tested.
  • There were no treatment-related effects on the uterine/implantation data, mean litter size and mean viable litter size.
  • There were no external abnormalities in live or dead pups in any of the groups.
  • No treatment-related changes in the ano-genital distance and ano-genital ratio were observed at any of the doses tested when compared to the vehicle control group.
  • The male pups did not exhibit areola/nipple retention on PND 13 at any of the doses tested.
  • The test item administration did not reveal any treatment related changes in the hematology, coagulation and clinical chemistry parameters of both males and females.
  • There were no test item related changes in the terminal body weights, organ weights and organs weight ratios in both males and females.
  • Gross pathological examination of pups on LD 13 did not reveal any gross changes.
  • There were no test item related gross and microscopic changes in both males and females. Microscopically in lungs, pigmented macrophages were observed at 1000 mg/kg Bwt/day in both sexes and considered as test item related non-adverse finding. This change showed complete recovery at the end of recovery period.
  • The thyroid stimulating hormone (TSH) and thyroxine (T4) levels in adult rats and pups remained unaffected by test item-administration.
  • No test item related changes were observed in organ weights, gross and histopathology of thyroid gland of parental rats and pups.

The No Observed Adverse Effect Level (NOAEL) of Hostaperm-Orange GR for general toxicity (repeated dose toxicity) in males and females is considered to be 1000 mg/kg Bwt/day.

Therefore, the test item has not to be classified as subacutely toxic (STOT RD) by the oral route according to Regulation (EC) No 1272/2008.

Endpoint:
short-term repeated dose toxicity: oral
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Guideline study – Read-across
Justification for type of information:
Please refer to attached read across justification document (Chapter 13).
Reason / purpose for cross-reference:
read-across source
Clinical signs:
no effects observed
Description (incidence and severity):
The orange coloured fecal pellets observed were due to the physical appearance of the test item, not related to the toxicity.
Mortality:
no mortality observed
Body weight and weight changes:
no effects observed
Food consumption and compound intake (if feeding study):
no effects observed
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
no effects observed
Description (incidence and severity):
eye examination: normal
Haematological findings:
no effects observed
Clinical biochemistry findings:
no effects observed
Urinalysis findings:
no effects observed
Behaviour (functional findings):
no effects observed
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Gross pathological findings:
no effects observed
Neuropathological findings:
no effects observed
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Microscopically, pigmented macrophages were observed in lungs at 1000 mg/kg bw/day in both sexes and considered as test item-related non-adverse finding. This change showed complete recovery at the end of recovery period.
Key result
Dose descriptor:
NOAEL
Effect level:
1 000 mg/kg bw/day (nominal)
Based on:
act. ingr.
Sex:
male/female
Basis for effect level:
other: highest dose applied
Key result
Critical effects observed:
no
Conclusions:
The substance is expected not to produce any signs of toxicity and a NOAEL of 1000 mg/kg bw is asumed.
Executive summary:

A read across was performed for this endpoint with Pigment Orange 43 as a source substance.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
1 000 mg/kg bw/day
Study duration:
subacute
Species:
rat
Quality of whole database:
reliable
System:
other: no system affected at the highest dose tested

Repeated dose toxicity: inhalation - systemic effects

Endpoint conclusion
Endpoint conclusion:
no study available

Repeated dose toxicity: inhalation - local effects

Endpoint conclusion
Endpoint conclusion:
no study available

Repeated dose toxicity: dermal - systemic effects

Endpoint conclusion
Endpoint conclusion:
no study available

Repeated dose toxicity: dermal - local effects

Endpoint conclusion
Endpoint conclusion:
no study available

Additional information

Justification for classification or non-classification

Repeated dose toxicity (STOT RE)

The NOAEL for repeated dose toxicity is below the threshold for classification.

Therefore, the Target Substance C.I. Pigment Red 194 has not to be classified for repeated dose toxicity (STOT RE) according to Regulation (EC) No 1272/2008.