NOAEL Studies
Cosmetic Ingredient
CURRY RED NOAEL Studies
CAS: 25956-17-6
Raw No Observed Adverse Effect Level endpoint records grouped by source. This page does not render calculated Margin of Safety values.
COSMOS_DB 16 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| COSMOS_DB | LOAEL | 250 | mg/kg bw/day | dog | oral | 42 day | Subchronic | PAFA |
| COSMOS_DB | NOAEL | 250 | mg/kg bw/day | dog | oral | 42 day | Short Term Toxicity | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 5190 | mg/kg bw/day | rat | oral | 42 day | Short Term Toxicity | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 2595 | mg/kg bw/day | rat | oral | 847 day | Chronic | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 7785 | mg/kg bw/day | mouse | oral | 728 day | Chronic | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 200 | mg/kg bw/day | rat | oral | 21 day | Developmental | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 1500 | mg/kg bw/day | swine | oral | 76 day | Short Term Toxicity | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 3604 | mg/kg bw/day | rat | oral | 847 day | Chronic | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 1000 | mg/kg bw/day | rat | oral | 20 day | Developmental | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 939.3 | mg/kg bw/day | rat | oral | 20 day | Reproductive-developmental | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 7422 | mg/kg bw/day | mouse | oral | 728 day | Carcinogenicity | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 7318 | mg/kg bw/day | mouse | oral | 763 day | Carcinogenicity | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 5000 | mg/kg bw/day | rat | oral | 14 day | Short Term Toxicity | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 2550 | mg/kg bw/day | mouse | oral | NA | Reproductive | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 700 | mg/kg bw/day | rabbit | oral | 13 day | Developmental | US FDA CFSAN PAFA; US FDA CFSAN PAFA Study |
| COSMOS_DB | NOAEL | 125 | mg/kg bw/day | dog | oral | 42 day | Subchronic | PAFA |
EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx 10 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | LOAEL | =50 | mg/kg bw/day | Mouse | - | - | reproduction toxicity | EFSA AFC - 2008 - OutputID 295 - neurology - developmental - Safety of aluminium from dietary intake - doi:10.2903/j.efsa.2008.754 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | LOAEL | =50 | mg/kg bw/day | Mouse | - | - | reproduction toxicity | EFSA AFC - 2008 - OutputID 295 - neurology - developmental - Safety of aluminium from dietary intake - doi:10.2903/j.efsa.2008.754 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =701 | mg/kg bw/day | Rat | oral: unspecified | - | chronic/long term toxicity | EFSA ANS - 2009 - OutputID 391 - body weight - systemic - Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive - doi:10.2903/j.efsa.2009.1327 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =695 | mg/kg bw/day | Rat | oral: unspecified | - | reproduction toxicity | EFSA ANS - 2009 - OutputID 391 - growth - developmental - Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive - doi:10.2903/j.efsa.2009.1327 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =13900 | mg/kg | Rat | - | - | reproduction toxicity | EFSA FEEDAP - 2021 - OutputID 4068 - reproduction - reproductive - Safety and efficacy of a feed additive consisting of Allura Red AC for small non-food-producing mammals and ornamental birds (Versele-Laga) - doi:10.2903/j.efsa.2021.6987 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =10 | mg/kg bw/day | Mouse | oral: feed | - | reproduction toxicity | EFSA AFC - 2008 - OutputID 295 - neurology - reproductive - Safety of aluminium from dietary intake - doi:10.2903/j.efsa.2008.754 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =701 | mg/kg bw/day | Rat | oral: unspecified | - | chronic/long term toxicity | EFSA ANS - 2009 - OutputID 391 - body weight - systemic - Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive - doi:10.2903/j.efsa.2009.1327 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =695 | mg/kg bw/day | Rat | oral: unspecified | - | reproduction toxicity | EFSA ANS - 2009 - OutputID 391 - growth - developmental - Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive - doi:10.2903/j.efsa.2009.1327 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =13900 | mg/kg | Rat | - | - | reproduction toxicity | EFSA FEEDAP - 2021 - OutputID 4068 - reproduction - reproductive - Safety and efficacy of a feed additive consisting of Allura Red AC for small non-food-producing mammals and ornamental birds (Versele-Laga) - doi:10.2903/j.efsa.2021.6987 |
| EFSA_OpenFoodTox_EFSA_ReferencePoints.xlsx | NOAEL | =10 | mg/kg bw/day | Mouse | oral: feed | - | reproduction toxicity | EFSA AFC - 2008 - OutputID 295 - neurology - reproductive - Safety of aluminium from dietary intake - doi:10.2903/j.efsa.2008.754 |
EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx 6 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx | ADI | =7 | mg/kg bw/day | Consumers | - | - | ADI | EFSA ANS - 2009 - OutputID 391 - Consumers - Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive - doi:10.2903/j.efsa.2009.1327 |
| EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx | ADI | =0.14 | mg/kg bw/day | Consumers | - | - | ADI | EFSA - 2018 - OutputID 3111 - Consumers - Peer review of the pesticide risk assessment of the active substance fosetyl - doi:10.2903/j.efsa.2018.5307 |
| EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx | ADI | =7 | mg/kg bw/day | Consumers | - | - | ADI | EFSA ANS - 2009 - OutputID 391 - Consumers - Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive - doi:10.2903/j.efsa.2009.1327 |
| EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx | ADI | =0.14 | mg/kg bw/day | Consumers | - | - | ADI | EFSA - 2018 - OutputID 3111 - Consumers - Peer review of the pesticide risk assessment of the active substance fosetyl - doi:10.2903/j.efsa.2018.5307 |
| EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx | ARfD | =0.14 | mg/kg bw | Consumers | - | - | ARfD | EFSA - 2018 - OutputID 3111 - Consumers - Peer review of the pesticide risk assessment of the active substance fosetyl - doi:10.2903/j.efsa.2018.5307 |
| EFSA_OpenFoodTox_EFSA_ReferenceValues.xlsx | ARfD | =0.14 | mg/kg bw | Consumers | - | - | ARfD | EFSA - 2018 - OutputID 3111 - Consumers - Peer review of the pesticide risk assessment of the active substance fosetyl - doi:10.2903/j.efsa.2018.5307 |
NTP_ICE_acute_oral 1 endpoint
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| NTP_ICE_acute_oral | LD50 | >10000 | mg/kg bw | Rat | oral | acute | Rat Acute Oral Toxicity | record_id=acute_oral_4744; row=7258; data_type=In Vivo; mixture=Chemical; chemical_name=Allura Red C.I.16035; preferred_name=Allura Red C.I.16035; dtxsid=DTXSID4024436; url_comptox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; url_cebs=https://doi.org/10.22427/NTP-DATA-DTXSID4024436; source_file=acute_oral.xlsx |
NTP_ICE_adme_parameters 2 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| NTP_ICE_adme_parameters | Clint | 0 | uL/min/10^6 cells | Human | - | - | Measured; httk, Human Hepatic Intrinsic Clearance | sheet=Data; excel_row=1732; Record_ID=adme_parameters_884; Data_Type=Measured; DTXSID=DTXSID4024436; Assay=httk, Human Hepatic Intrinsic Clearance; Endpoint=Clint; Response=0.0; Response_Unit=ul/min/10^6 cells; Species=Human; Reference=httk2.3.1, Wambaugh 2019; URL=https://cran.r-project.org/web/packages/httk/index.html; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; URL_CEBS=https://doi.org/10.22427/NTP-DATA-DTXSID4024436 |
| NTP_ICE_adme_parameters | Fu | 0.0137 | fraction | Human | - | - | Measured; httk, Human Plasma Fraction Unbound | sheet=Data; excel_row=1731; Record_ID=adme_parameters_884; Data_Type=Measured; DTXSID=DTXSID4024436; Assay=httk, Human Plasma Fraction Unbound; Endpoint=Fu; Response=0.0137; Response_Unit=Unitless Fraction; Species=Human; Reference=httk2.3.1, Wambaugh 2019; URL=https://cran.r-project.org/web/packages/httk/index.html; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; URL_CEBS=https://doi.org/10.22427/NTP-DATA-DTXSID4024436 |
NTP_ICE_endocrine 4 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| NTP_ICE_endocrine | AC50 | 57.1229775240489 | uM | - | - | - | ERPathway2016; ER Pathway Model, Agonist | sheet=Integrated_approaches; excel_row=4734; RecordID=ERPathway2016_110; DatasetName=ERPathway2016; DTXSID=DTXSID4024436; Assay=ER Pathway Model, Agonist; Endpoint=AC50; Response=57.1229775240489; Response_Unit=uM; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; URL_CEBS=https://doi.org/10.22427/NTP-DATA-DTXSID4024436 |
| NTP_ICE_endocrine | ACC | 63.4118100206417 | uM | - | - | - | ERPathway2016; ER Pathway Model, Agonist | sheet=Integrated_approaches; excel_row=4735; RecordID=ERPathway2016_110; DatasetName=ERPathway2016; DTXSID=DTXSID4024436; Assay=ER Pathway Model, Agonist; Endpoint=ACC; Response=63.4118100206417; Response_Unit=uM; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; URL_CEBS=https://doi.org/10.22427/NTP-DATA-DTXSID4024436 |
| NTP_ICE_endocrine | Model Score | 0 | unitless | - | - | - | ARPathway2016; AR Pathway Model, Antagonist | sheet=Integrated_approaches; excel_row=4730; RecordID=ARPathway2016_1063; DatasetName=ARPathway2016; DTXSID=DTXSID4024436; Assay=AR Pathway Model, Antagonist; Endpoint=Model Score; Response=0; Response_Unit=Unitless; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; URL_CEBS=https://doi.org/10.22427/NTP-DATA-DTXSID4024436 |
| NTP_ICE_endocrine | Model Score | 0.0157 | unitless | - | - | - | ERPathway2016; ER Pathway Model, Antagonist | sheet=Integrated_approaches; excel_row=4737; RecordID=ERPathway2016_110; DatasetName=ERPathway2016; DTXSID=DTXSID4024436; Assay=ER Pathway Model, Antagonist; Endpoint=Model Score; Response=0.0157; Response_Unit=Unitless; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID4024436; URL_CEBS=https://doi.org/10.22427/NTP-DATA-DTXSID4024436 |
SCCNFP_vision_codex 40 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| SCCNFP_vision_codex | NOAEL | =50 | mg/kg bw/day | rat | oral | 6-week | repeated dose toxicity | {"citation":"Ref.: 2 2","dose":"Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.:","effect":"2, 3). 2.3. Toxicity 2.3.1. Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.: 2 2.3.2. Acute dermal toxicity No data 2.3.3. Acute inhalation toxicity No data 2.3.4. Repeated dose oral toxicity Mouse In a 6-week drinking water study groups of six male per group received doses of 0, 0.05 and 0.25 mg/ml Curry Red respectively in the drinking water. Bodyweight, drinking water consumption and investigations of brain, kidney, liver and spleen revealed no substance-related effects. A NOEL of 0.25 mg/ml in drinking water (equal to about 50 mg/kg bw/day, assuming a bodyweight of 25 g and a drinking water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals abou","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_001"} |
| SCCNFP_vision_codex | NOAEL | =3750 | mg/kg bw/day | rat | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_002"} |
| SCCNFP_vision_codex | NOAEL | =500 | mg/kg bw/day | dog | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"rified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_003"} |
| SCCNFP_vision_codex | NOAEL | =5.19 | % | dog | oral | 1 year | NOAEL study | {"dose":"From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"d, respectively, were fed to groups of four dogs (two female/two male) each. Eight animals (four per sex) were used for the concurrent control group. An interim sacrifice took place after 1 year (one animal per sex and group). Behaviour and clinical chemistry as well as macroscopic and microscopic investigations were performed. Besides some not further specified tissue effects after 1 year which were not seen after the final 2-year treatment no substance related effects were noted. From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_004"} |
| SCCNFP_vision_codex | NOAEL | =1500 | mg/kg bw/day | pig | oral | 21 days | repeated dose toxicity | {"dose":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance related effects. For the described exposure scenario a NOAEL in pigs of 1500 mg/kg bw/day can be assumed. 2.3.5 Repeated dose dermal toxicity No data 2.3.6. Repeated dose inhalation toxicity No data 2.3.7. Subchronic oral toxicity See 2.3.4 2.3.8. Sub-chronic dermal toxicity No data 2.3.9. Sub-chronic inhalation toxicity No data 2.3.10. Chronic toxicity See also point 2.9. (combination studies chronic toxicity/carcinogenicity)","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_005"} |
| SCCNFP_vision_codex | NOAEL | =1000 | mg/kg bw/day | rat | - | prenatal | developmental toxicity | {"citation":"Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited","dose":"In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic.","effect":"of these variations were therefore considered to be accidental, moreover as they were within the historical controls range. In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic. Neither in the dams nor in the foetuses indications were noted for treatment-related adverse effects. Thus, for both the maternal and developmental toxicity a NOEL of ≥ 1000 mg/kg bw/day can be deduced from this study. Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited. Based on this information Curry Red is not a teratogen in rabbits (cited in reference 5) and no embryo-, foetotoxic or teratogenic effects were noted in rats treated during pregnancy with up to 200 mg/kg bw/day; highest dose tested in this test (cited in reference 2). Furthermore, the findings of a 2-generation study in rats are summarised in the mentio","page":12,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_006"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg | dog | oral | - | NOAEL study | {"dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","effect":"ndicate a weekly use of 35 ml for a semi-permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic poten","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_007"} |
| SCCNFP_vision_codex | NOAEL | =1.39 | % | - | oral | - | carcinogenicity | {"dose":"In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species.","effect":"ng together all available data obtained with different species under different exposure scenarios. In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_010"} |
| SCCNFP_vision_codex | NOAEL | =7 | mg/kg bw/day | - | oral | - | carcinogenicity | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"endent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_011"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg bw/day | - | oral | - | NOAEL study | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_013"} |
| SCCNFP_vision_codex | NOAEL | =50 | mg/kg bw/day | rat | oral | 6-week | repeated dose toxicity | {"citation":"Ref.: 2 2","dose":"Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.:","effect":"2, 3). 2.3. Toxicity 2.3.1. Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.: 2 2.3.2. Acute dermal toxicity No data 2.3.3. Acute inhalation toxicity No data 2.3.4. Repeated dose oral toxicity Mouse In a 6-week drinking water study groups of six male per group received doses of 0, 0.05 and 0.25 mg/ml Curry Red respectively in the drinking water. Bodyweight, drinking water consumption and investigations of brain, kidney, liver and spleen revealed no substance-related effects. A NOEL of 0.25 mg/ml in drinking water (equal to about 50 mg/kg bw/day, assuming a bodyweight of 25 g and a drinking water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals abou","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_001"} |
| SCCNFP_vision_codex | NOAEL | =3750 | mg/kg bw/day | rat | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_002"} |
| SCCNFP_vision_codex | NOAEL | =500 | mg/kg bw/day | dog | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"rified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_003"} |
| SCCNFP_vision_codex | NOAEL | =5.19 | % | dog | oral | 1 year | NOAEL study | {"dose":"From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"d, respectively, were fed to groups of four dogs (two female/two male) each. Eight animals (four per sex) were used for the concurrent control group. An interim sacrifice took place after 1 year (one animal per sex and group). Behaviour and clinical chemistry as well as macroscopic and microscopic investigations were performed. Besides some not further specified tissue effects after 1 year which were not seen after the final 2-year treatment no substance related effects were noted. From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_004"} |
| SCCNFP_vision_codex | NOAEL | =1500 | mg/kg bw/day | pig | oral | 21 days | repeated dose toxicity | {"dose":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance related effects. For the described exposure scenario a NOAEL in pigs of 1500 mg/kg bw/day can be assumed. 2.3.5 Repeated dose dermal toxicity No data 2.3.6. Repeated dose inhalation toxicity No data 2.3.7. Subchronic oral toxicity See 2.3.4 2.3.8. Sub-chronic dermal toxicity No data 2.3.9. Sub-chronic inhalation toxicity No data 2.3.10. Chronic toxicity See also point 2.9. (combination studies chronic toxicity/carcinogenicity)","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_005"} |
| SCCNFP_vision_codex | NOAEL | =1000 | mg/kg bw/day | rat | - | prenatal | developmental toxicity | {"citation":"Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited","dose":"In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic.","effect":"of these variations were therefore considered to be accidental, moreover as they were within the historical controls range. In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic. Neither in the dams nor in the foetuses indications were noted for treatment-related adverse effects. Thus, for both the maternal and developmental toxicity a NOEL of ≥ 1000 mg/kg bw/day can be deduced from this study. Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited. Based on this information Curry Red is not a teratogen in rabbits (cited in reference 5) and no embryo-, foetotoxic or teratogenic effects were noted in rats treated during pregnancy with up to 200 mg/kg bw/day; highest dose tested in this test (cited in reference 2). Furthermore, the findings of a 2-generation study in rats are summarised in the mentio","page":12,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_006"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg | dog | oral | - | NOAEL study | {"dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","effect":"ndicate a weekly use of 35 ml for a semi-permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic poten","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_007"} |
| SCCNFP_vision_codex | NOAEL | =1.39 | % | - | oral | - | carcinogenicity | {"dose":"In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species.","effect":"ng together all available data obtained with different species under different exposure scenarios. In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_010"} |
| SCCNFP_vision_codex | NOAEL | =7 | mg/kg bw/day | - | oral | - | carcinogenicity | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"endent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_011"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg bw/day | - | oral | - | NOAEL study | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_013"} |
| SCCNFP_vision_codex | NOAEL | =50 | mg/kg bw/day | rat | oral | 6-week | repeated dose toxicity | {"citation":"Ref.: 2 2","dose":"Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.:","effect":"2, 3). 2.3. Toxicity 2.3.1. Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.: 2 2.3.2. Acute dermal toxicity No data 2.3.3. Acute inhalation toxicity No data 2.3.4. Repeated dose oral toxicity Mouse In a 6-week drinking water study groups of six male per group received doses of 0, 0.05 and 0.25 mg/ml Curry Red respectively in the drinking water. Bodyweight, drinking water consumption and investigations of brain, kidney, liver and spleen revealed no substance-related effects. A NOEL of 0.25 mg/ml in drinking water (equal to about 50 mg/kg bw/day, assuming a bodyweight of 25 g and a drinking water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals abou","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_001"} |
| SCCNFP_vision_codex | NOAEL | =3750 | mg/kg bw/day | rat | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_002"} |
| SCCNFP_vision_codex | NOAEL | =500 | mg/kg bw/day | dog | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"rified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_003"} |
| SCCNFP_vision_codex | NOAEL | =5.19 | % | dog | oral | 1 year | NOAEL study | {"dose":"From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"d, respectively, were fed to groups of four dogs (two female/two male) each. Eight animals (four per sex) were used for the concurrent control group. An interim sacrifice took place after 1 year (one animal per sex and group). Behaviour and clinical chemistry as well as macroscopic and microscopic investigations were performed. Besides some not further specified tissue effects after 1 year which were not seen after the final 2-year treatment no substance related effects were noted. From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_004"} |
| SCCNFP_vision_codex | NOAEL | =1500 | mg/kg bw/day | pig | oral | 21 days | repeated dose toxicity | {"dose":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance related effects. For the described exposure scenario a NOAEL in pigs of 1500 mg/kg bw/day can be assumed. 2.3.5 Repeated dose dermal toxicity No data 2.3.6. Repeated dose inhalation toxicity No data 2.3.7. Subchronic oral toxicity See 2.3.4 2.3.8. Sub-chronic dermal toxicity No data 2.3.9. Sub-chronic inhalation toxicity No data 2.3.10. Chronic toxicity See also point 2.9. (combination studies chronic toxicity/carcinogenicity)","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_005"} |
| SCCNFP_vision_codex | NOAEL | =1000 | mg/kg bw/day | rat | - | prenatal | developmental toxicity | {"citation":"Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited","dose":"In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic.","effect":"of these variations were therefore considered to be accidental, moreover as they were within the historical controls range. In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic. Neither in the dams nor in the foetuses indications were noted for treatment-related adverse effects. Thus, for both the maternal and developmental toxicity a NOEL of ≥ 1000 mg/kg bw/day can be deduced from this study. Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited. Based on this information Curry Red is not a teratogen in rabbits (cited in reference 5) and no embryo-, foetotoxic or teratogenic effects were noted in rats treated during pregnancy with up to 200 mg/kg bw/day; highest dose tested in this test (cited in reference 2). Furthermore, the findings of a 2-generation study in rats are summarised in the mentio","page":12,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_006"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg | dog | oral | - | NOAEL study | {"dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","effect":"ndicate a weekly use of 35 ml for a semi-permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic poten","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_007"} |
| SCCNFP_vision_codex | NOAEL | =1.39 | % | - | oral | - | carcinogenicity | {"dose":"In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species.","effect":"ng together all available data obtained with different species under different exposure scenarios. In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_010"} |
| SCCNFP_vision_codex | NOAEL | =7 | mg/kg bw/day | - | oral | - | carcinogenicity | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"endent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_011"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg bw/day | - | oral | - | NOAEL study | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_013"} |
| SCCNFP_vision_codex | NOAEL | =50 | mg/kg bw/day | rat | oral | 6-week | repeated dose toxicity | {"citation":"Ref.: 2 2","dose":"Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.:","effect":"2, 3). 2.3. Toxicity 2.3.1. Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.: 2 2.3.2. Acute dermal toxicity No data 2.3.3. Acute inhalation toxicity No data 2.3.4. Repeated dose oral toxicity Mouse In a 6-week drinking water study groups of six male per group received doses of 0, 0.05 and 0.25 mg/ml Curry Red respectively in the drinking water. Bodyweight, drinking water consumption and investigations of brain, kidney, liver and spleen revealed no substance-related effects. A NOEL of 0.25 mg/ml in drinking water (equal to about 50 mg/kg bw/day, assuming a bodyweight of 25 g and a drinking water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals abou","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_001"} |
| SCCNFP_vision_codex | NOAEL | =3750 | mg/kg bw/day | rat | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_002"} |
| SCCNFP_vision_codex | NOAEL | =500 | mg/kg bw/day | dog | oral | 14 days | NOAEL study | {"citation":"Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","effect":"rified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","page":6,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_003"} |
| SCCNFP_vision_codex | NOAEL | =5.19 | % | dog | oral | 1 year | NOAEL study | {"dose":"From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"d, respectively, were fed to groups of four dogs (two female/two male) each. Eight animals (four per sex) were used for the concurrent control group. An interim sacrifice took place after 1 year (one animal per sex and group). Behaviour and clinical chemistry as well as macroscopic and microscopic investigations were performed. Besides some not further specified tissue effects after 1 year which were not seen after the final 2-year treatment no substance related effects were noted. From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_004"} |
| SCCNFP_vision_codex | NOAEL | =1500 | mg/kg bw/day | pig | oral | 21 days | repeated dose toxicity | {"dose":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","effect":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance related effects. For the described exposure scenario a NOAEL in pigs of 1500 mg/kg bw/day can be assumed. 2.3.5 Repeated dose dermal toxicity No data 2.3.6. Repeated dose inhalation toxicity No data 2.3.7. Subchronic oral toxicity See 2.3.4 2.3.8. Sub-chronic dermal toxicity No data 2.3.9. Sub-chronic inhalation toxicity No data 2.3.10. Chronic toxicity See also point 2.9. (combination studies chronic toxicity/carcinogenicity)","page":7,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_005"} |
| SCCNFP_vision_codex | NOAEL | =1000 | mg/kg bw/day | rat | - | prenatal | developmental toxicity | {"citation":"Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited","dose":"In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic.","effect":"of these variations were therefore considered to be accidental, moreover as they were within the historical controls range. In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic. Neither in the dams nor in the foetuses indications were noted for treatment-related adverse effects. Thus, for both the maternal and developmental toxicity a NOEL of ≥ 1000 mg/kg bw/day can be deduced from this study. Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited. Based on this information Curry Red is not a teratogen in rabbits (cited in reference 5) and no embryo-, foetotoxic or teratogenic effects were noted in rats treated during pregnancy with up to 200 mg/kg bw/day; highest dose tested in this test (cited in reference 2). Furthermore, the findings of a 2-generation study in rats are summarised in the mentio","page":12,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_006"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg | dog | oral | - | NOAEL study | {"dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","effect":"ndicate a weekly use of 35 ml for a semi-permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic poten","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_007"} |
| SCCNFP_vision_codex | NOAEL | =1.39 | % | - | oral | - | carcinogenicity | {"dose":"In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species.","effect":"ng together all available data obtained with different species under different exposure scenarios. In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_010"} |
| SCCNFP_vision_codex | NOAEL | =7 | mg/kg bw/day | - | oral | - | carcinogenicity | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"endent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_011"} |
| SCCNFP_vision_codex | NOAEL | =700 | mg/kg bw/day | - | oral | - | NOAEL study | {"dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","effect":"this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.","page":19,"pdf":"out264_en.pdf","row_type":"noael_study","study_id":"out264_en_noael_013"} |
ToxValDB_ECHA_IUCLID 5 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| ToxValDB_ECHA_IUCLID | NOAEL | =260.2 | mg/kg bw/day | Rat | oral | - | reproduction developmental | QUALITY=2 (reliable with restrictions); STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/669eac26e4b0a7c65d1bdaaa; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://echa.europa.eu/; SUBSOURCE_URL=https://echa.europa.eu/registration-dossier/-/registered-dossier/17284/7/9/3?documentUUID=4ef657bb-2068-4ffe-ae1d-0d0d195e59c0; YEAR=2016; ORIGINAL_YEAR=2016; STUDY_GROUP=ECHA IUCLID:15823265:F:-maternal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_ce8d0b033fc53591e0682796393538ac |
| ToxValDB_ECHA_IUCLID | NOAEL | =200 | mg/kg bw/day | Rat | oral | - | developmental | QUALITY=2 (reliable with restrictions); STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/669eac26e4b0a7c65d1bdaa4; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://echa.europa.eu/; SUBSOURCE_URL=https://echa.europa.eu/registration-dossier/-/registered-dossier/17284/7/9/3?documentUUID=4ef657bb-2068-4ffe-ae1d-0d0d195e59c0; YEAR=2016; ORIGINAL_YEAR=2016; STUDY_GROUP=ECHA IUCLID:15823529:-:-fetal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_85663e4e89b28f76b90f934ded2ac524 |
| ToxValDB_ECHA_IUCLID | NOAEL | =1000 | mg/kg bw/day | Rat | oral | - | reproduction developmental | QUALITY=2 (reliable with restrictions); STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/669eac0de4b0a7c65d1bd2db; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://echa.europa.eu/; SUBSOURCE_URL=https://echa.europa.eu/registration-dossier/-/registered-dossier/11604/7/9/3?documentUUID=17a6d5cd-1cbd-41b3-b200-263e0a0215cb; YEAR=1980; ORIGINAL_YEAR=1980; STUDY_GROUP=ECHA IUCLID:15824706:F:-maternal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_ac3438077009d6b72a525a2c41367859 |
| ToxValDB_ECHA_IUCLID | NOAEL | =901 | mg/kg bw/day | Rat | oral | chronic; 121 weeks | chronic | QUALITY=2 (reliable with restrictions); STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/669ead10e4b0a7c65d1c2564; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://echa.europa.eu/; SUBSOURCE_URL=https://echa.europa.eu/en/registration-dossier/-/registered-dossier/12236?documentUUID=99b7317c-4c1d-4b46-8d69-c269b8cd8271; YEAR=2019; ORIGINAL_YEAR=2019; TOXICOLOGICAL_EFFECT=body weight and weight gain; TOXICOLOGICAL_EFFECT_CATEGORY=body weight; STUDY_GROUP=ECHA IUCLID:15847777:F:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_569b0c0e066c4924dcd7b695f383f204 |
| ToxValDB_ECHA_IUCLID | NOAEL | =2829 | mg/kg bw/day | Rat | oral | chronic; 118 weeks | chronic | QUALITY=2 (reliable with restrictions); STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/669ead10e4b0a7c65d1c2564; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://echa.europa.eu/; SUBSOURCE_URL=https://echa.europa.eu/en/registration-dossier/-/registered-dossier/12236?documentUUID=99b7317c-4c1d-4b46-8d69-c269b8cd8271; YEAR=2019; ORIGINAL_YEAR=2019; STUDY_GROUP=ECHA IUCLID:15850590:M:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_c3d6967638d07309d964cafb0ee729e6 |
ToxValDB_ECOTOX 2 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| ToxValDB_ECOTOX | LOEL | =10 | mg/kg bw/day | Mouse | oral | acute; 1 days | acute | LONG_REF=Mutat. Res.519(1/2): 103-119 Sasaki,Y.F., S. Kawaguchi, A. Kamaya, M. Ohshita, K. Kabasawa, K. Iwama, K. Taniguchi, and S. Tsuda The Comet Assay with 8 Mouse Organs: Results with 39 Currently Used Food Additives 2002; TITLE=The Comet Assay with 8 Mouse Organs: Results with 39 Currently Used Food Additives; AUTHOR=Sasaki,Y.F., S. Kawaguchi, A. Kamaya, M. Ohshita, K. Kabasawa, K. Iwama, K. Taniguchi, and S. Tsuda; DOI=10.1016/s1383-5718(02)00128-6; QUALITY=Control type: Concurrent control; EXTERNAL_SOURCE_ID=75840; EXTERNAL_SOURCE_ID_DESC=ECOTOX Reference Number; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/6759bce8e4b0a7c65d37bc5f; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://cfpub.epa.gov/ecotox/; YEAR=2002; ORIGINAL_YEAR=2002; TOXICOLOGICAL_EFFECT=Genetics: Damage; TOXICOLOGICAL_EFFECT_CATEGORY=other; STUDY_GROUP=ECOTOX_dup_EPA ORD_15597275_15597276:M:--; QC_CATEGORY=Data source QC'd by data provider prior to ECOTOX import; QC_STATUS=not determined; SOURCE_HASH=f03ea79a82ef88eb18595d3e52aabf1e |
| ToxValDB_ECOTOX | NOEL | =1 | mg/kg bw/day | Mouse | oral | acute; 1 days | acute | LONG_REF=Mutat. Res.519(1/2): 103-119 Sasaki,Y.F., S. Kawaguchi, A. Kamaya, M. Ohshita, K. Kabasawa, K. Iwama, K. Taniguchi, and S. Tsuda The Comet Assay with 8 Mouse Organs: Results with 39 Currently Used Food Additives 2002; TITLE=The Comet Assay with 8 Mouse Organs: Results with 39 Currently Used Food Additives; AUTHOR=Sasaki,Y.F., S. Kawaguchi, A. Kamaya, M. Ohshita, K. Kabasawa, K. Iwama, K. Taniguchi, and S. Tsuda; DOI=10.1016/s1383-5718(02)00128-6; QUALITY=Control type: Concurrent control; EXTERNAL_SOURCE_ID=75840; EXTERNAL_SOURCE_ID_DESC=ECOTOX Reference Number; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/6759bce8e4b0a7c65d37bc5f; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://cfpub.epa.gov/ecotox/; YEAR=2002; ORIGINAL_YEAR=2002; TOXICOLOGICAL_EFFECT=Genetics: Damage; TOXICOLOGICAL_EFFECT_CATEGORY=other; STUDY_GROUP=ECOTOX_dup_EPA ORD_15597275_15597276:M:--; QC_CATEGORY=Data source QC'd by data provider prior to ECOTOX import; QC_STATUS=not determined; SOURCE_HASH=f2859d07d0110c4e3e70fb3be0e6267b |
ToxValDB_EFSA 2 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| ToxValDB_EFSA | NOAEL | =695 | mg/kg bw/day | Rat | oral | - | reproduction developmental | LONG_REF=EFSA ANS (2009). Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive. doi:10.2903/j.efsa.2009.1327.; TITLE=Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive; AUTHOR=EFSA ANS; DOI=doi:10.2903/j.efsa.2009.1327; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/65201d30e4b0f0a60ddd1165; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://zenodo.org/record/5076033#.Y9fEoXbMI2z; YEAR=2009; ORIGINAL_YEAR=2009; TOXICOLOGICAL_EFFECT=growth; TOXICOLOGICAL_EFFECT_CATEGORY=development; STUDY_GROUP=EFSA:15614076:M/F:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_ab205ca464e4f57c37f757f3f6d89f17 |
| ToxValDB_EFSA | NOAEL | =701 | mg/kg bw/day | Rat | oral | - | chronic | LONG_REF=EFSA ANS (2009). Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive. doi:10.2903/j.efsa.2009.1327.; TITLE=Scientific Opinion on the re-evaluation of Allura Red AC (E 129) as a food additive; AUTHOR=EFSA ANS; DOI=doi:10.2903/j.efsa.2009.1327; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/65201d30e4b0f0a60ddd1165; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://zenodo.org/record/5076033#.Y9fEoXbMI2z; YEAR=2009; ORIGINAL_YEAR=2009; TOXICOLOGICAL_EFFECT=body weight; TOXICOLOGICAL_EFFECT_CATEGORY=body weight; STUDY_GROUP=EFSA:15614077:M/F:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_28b89b1a96c261f601c5bdbf337637f9 |
ToxValDB_GESTIS_DNEL 1 endpoint
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| ToxValDB_GESTIS_DNEL | DNEL systemic | =16.4 | mg/m3 | Human | inhalation | - | Toxicity Value | STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/6543dd69e4b045b9ff7cd87e; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://www.dguv.de/ifa/gestis/gestis-dnel-liste/index-2.jsp; STUDY_GROUP=GESTIS DNEL:15631641:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_1b60b2d366262f90a31ef05e9294233e |
ToxValDB_HPVIS 9 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| ToxValDB_HPVIS | LOAEL | >2829 | mg/kg bw/day | Rat | oral | chronic; 118 weeks | reproduction developmental | LONG_REF=Borzelleca J.F., Olson J.W. and Reno F.E. (1991a) Lifetime toxicity/ carcinogenicity studies of FD&C Red No. 40 (Allura Red) in Sprague Dawley Rats. Food and Chemical Toxicology, 27, 701-705.Posting dates of the documents from the HPV Challenge Program website from which data have been entered into the HPVIS:Test Plan: Dec. 12, 2006; CBIC Received: Nov. 13, 2006Robust Summary: Dec. 12, 2006; CBIC Received: Nov. 13, 2006. Study is also summarized in the initial robust summary posted Dec. 17, 2003.; QUALITY=1; EXTERNAL_SOURCE_ID=61953; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480596; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1991; ORIGINAL_YEAR=1991; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Repeat Dose_15639253_15639304:M:-paternal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_b3d44474749b38af6d1ca91b267b7ba3 |
| ToxValDB_HPVIS | LOAEL | =3604 | mg/kg bw/day | Rat | oral | chronic; 118 weeks | chronic | LONG_REF=Borzelleca J.F., Olson J.W. and Reno F.E. (1991a) Lifetimetoxicity/ carcinogenicity studies of FD&C Red No. 40 (AlluraRed) in Sprague Dawley Rats. Food and Chemical Toxicology, 27, 701-705.Data extracted from the robust summary posted to the HPV Challenge Program website Dec. 22, 2006.; QUALITY=1; EXTERNAL_SOURCE_ID=62758; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480596; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1991; ORIGINAL_YEAR=1991; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Repeat Dose_15639334_15639335:F:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_ffbebc819aafec5e1b3518a88e35b887 |
| ToxValDB_HPVIS | LOAEL | =545.68 | mg/kg bw/day | Rat | oral | short-term; 20 days | reproduction developmental | LONG_REF=Collins T., Black T.N., Welsch J.J., and Brown L.H. (1989a) Study of the teratogenic potential of FD & C Red No. 40 when given in drinking water. Toxicology and Industrial Health 5, 937-948.Posting dates of the documents from the HPV Challenge Program website from which data have been entered into the HPVIS:Test Plan: Dec. 12, 2006; CBIC Received: Nov. 13, 2006Robust Summary: Dec. 12, 2006; CBIC Received: Nov. 13, 2006. Study is also summarized in the initial robust summary posted Dec. 17, 2003.; QUALITY=1; EXTERNAL_SOURCE_ID=58378; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480590; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1989; ORIGINAL_YEAR=1989; STUDY_GROUP=HPVIS:15642432:-:F1offspring; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_9e09b413a9ab9a829b4e78b3ceab64da |
| ToxValDB_HPVIS | LOAEL | =51900 | ppm | Rat | oral | - | reproduction developmental | LONG_REF=Hazelton Laboratories Inc. (1969) Two-generation reproductive study in rats. Red Z4576 (FD&C Red 40). Unpublished report 165-125.Data extracted from the robust summary posted to the HPV Challenge Program website Dec. 22, 2006.; QUALITY=1; EXTERNAL_SOURCE_ID=65291; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480598; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1969; ORIGINAL_YEAR=1969; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Reprotox_15643168_15643169:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_7aa59f81ab49a396a352ae7fd50725cd |
| ToxValDB_HPVIS | NOAEL | >5.19 | % diet | Mouse | oral | chronic; 104 weeks | chronic | LONG_REF=Borzelleca J.F., Olson J.W. and Reno F.E. (1991b) Lifetime toxicity/ carcinogenicity studies of FD&C Red No. 40 (Allura Red) in mice. Food and Chemical Toxicology, 29, 313-319.Data extracted from the robust summary posted to the HPV Challenge Program website Dec. 22, 2006.; QUALITY=1; EXTERNAL_SOURCE_ID=60646; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480596; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1991; ORIGINAL_YEAR=1991; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Repeat Dose_15639083_15639185:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_91fa6f06a7ad778e73bb5d1e8d5ab761 |
| ToxValDB_HPVIS | NOAEL | =901 | mg/kg bw/day | Rat | oral | chronic; 118 weeks | reproduction developmental | LONG_REF=Borzelleca J.F., Olson J.W. and Reno F.E. (1991a) Lifetime toxicity/ carcinogenicity studies of FD&C Red No. 40 (Allura Red) in Sprague Dawley Rats. Food and Chemical Toxicology, 27, 701-705.Posting dates of the documents from the HPV Challenge Program website from which data have been entered into the HPVIS:Test Plan: Dec. 12, 2006; CBIC Received: Nov. 13, 2006Robust Summary: Dec. 12, 2006; CBIC Received: Nov. 13, 2006. Study is also summarized in the initial robust summary posted Dec. 17, 2003.; QUALITY=1; EXTERNAL_SOURCE_ID=63269; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480596; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1991; ORIGINAL_YEAR=1991; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Repeat Dose_15639388_15639416:F:-maternal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_a4ca51ab75224de5cc8a44f211bf1c54 |
| ToxValDB_HPVIS | NOAEL | =939.29 | mg/kg bw/day | Rat | oral | short-term; 20 days | reproduction developmental | LONG_REF=Collins T., Black T.N., Welsch J.J., and Brown L.H. (1989a) Study of the teratogenic potential of FD & C Red No. 40 when given in drinking water. Toxicology and Industrial Health 5, 937-948.Posting dates of the documents from the HPV Challenge Program website from which data have been entered into the HPVIS:Test Plan: Dec. 12, 2006; CBIC Received: Nov. 13, 2006Robust Summary: Dec. 12, 2006; CBIC Received: Nov. 13, 2006. Study is also summarized in the initial robust summary posted Dec. 17, 2003.; QUALITY=1; EXTERNAL_SOURCE_ID=58377; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480590; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1989; ORIGINAL_YEAR=1989; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Devtox_15642431_15642689:F:-maternal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_1bfba8bdabfad08e294c357beb38279a |
| ToxValDB_HPVIS | NOAEL | =273.58 | mg/kg bw/day | Rat | oral | short-term; 20 days | developmental | LONG_REF=Collins T., Black T.N., Welsch J.J., and Brown L.H. (1989a) Study of the teratogenic potential of FD & C Red No. 40 when given in drinking water. Toxicology and Industrial Health 5, 937-948.Data extracted from the robust summary posted to the HPV Challenge Program website Dec. 22, 2006.; QUALITY=1; EXTERNAL_SOURCE_ID=59595; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480590; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1989; ORIGINAL_YEAR=1989; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Devtox_15642798_15642927:-:-fetal; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, and this record was expert reviewed; QC_STATUS=pass; SOURCE_HASH=ToxValhc_e03112f87a55b9b3bfbc6b5a9d2cf7bf |
| ToxValDB_HPVIS | NOAEL | =13900 | ppm | Rat | oral | - | reproduction developmental | LONG_REF=Hazelton Laboratories Inc. (1969) Two-generation reproductive study in rats. Red Z4576 (FD&C Red 40). Unpublished report 165-125.Data extracted from the robust summary posted to the HPV Challenge Program website Dec. 22, 2006.; QUALITY=1; EXTERNAL_SOURCE_ID=65290; EXTERNAL_SOURCE_ID_DESC=HPVIS ID; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/63861d6de4b04f6bb1480598; RECORD_SOURCE_LEVEL=Extraction document; YEAR=1969; ORIGINAL_YEAR=1969; STUDY_GROUP=HPVIS_dup_HPVIS Mammalian Reprotox_15643168_15643169:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_0138e572caeedbcc487fb65df8119910 |
ToxValDB_WHO_JECFA_ADI 1 endpoint
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| ToxValDB_WHO_JECFA_ADI | ADI | <=7 | mg/kg | Human | oral | - | Toxicity Value | STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/650af6c4e4b0d99f5a875bc9; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://apps.who.int/food-additives-contaminants-jecfa-database/; SUBSOURCE_URL=https://apps.who.int/food-additives-contaminants-jecfa-database/Home/Chemical/2361; YEAR=1981; ORIGINAL_YEAR=1981; STUDY_GROUP=WHO JECFA ADI:15715299:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_8d79c69f96873097eddcb2b00ccfe4e9 |
UnifiedCodex:SCCNFP:beta.noael_studies 14 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| UnifiedCodex:SCCNFP:beta.noael_studies | - | 3750 | mg/kg bw/day | rat | oral | 14 days | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=3750; DOSE=Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.; EFFECT=water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.; CITATION=Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5; CITATION_NUMBERS=[2,6,5]; REFERENCE=Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5; DETAILS_JSON={"cas_number":"25956-17-6","citation":"Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","duration":"14 days","effect":"water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"3750","page":6,"route":"oral","species":"rat","study_id":"out264_en_noael_002"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | 500 | mg/kg bw/day | dog | oral | 14 days | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=500; DOSE=Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.; EFFECT=rified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.; CITATION=Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights; CITATION_NUMBERS=[2,6,125,250,500]; REFERENCE=Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights; DETAILS_JSON={"cas_number":"25956-17-6","citation":"Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights","dose":"Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived.","duration":"14 days","effect":"rified diet. Based on this study administering 5 % Curry Red in the diet (equals about 3750 mg/kg bw/day, assuming an average bodyweight of 200 g and a food consumption of 15 g/day) for 14 days a NOAEL of about 3750 mg/kg bw/day can be derived. Ref.: 2 Dog In dogs (one female, one male), the oral administration of Curry Red for 6 weeks at doses of 125, 250 and 500 mg/kg bw/day did not effect the body and organ weights. Clinical, macroscopic and microscopic investigations did not reveal substance related effects; a NOEL of 500 mg/kg bw/day for the dog can be deduced.","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"500","page":6,"route":"oral","species":"dog","study_id":"out264_en_noael_003"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | 5.19 | % | dog | oral | 1 year | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=5.19; DOSE=From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).; EFFECT=d, respectively, were fed to groups of four dogs (two female/two male) each. Eight animals (four per sex) were used for the concurrent control group. An interim sacrifice took place after 1 year (one animal per sex and group). Behaviour and clinical chemistry as well as macroscopic and microscopic investigations were performed. Besides some not further specified tissue effects after 1 year which were not seen after the final 2-year treatment no substance related effects were noted. From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","duration":"1 year","effect":"d, respectively, were fed to groups of four dogs (two female/two male) each. Eight animals (four per sex) were used for the concurrent control group. An interim sacrifice took place after 1 year (one animal per sex and group). Behaviour and clinical chemistry as well as macroscopic and microscopic investigations were performed. Besides some not further specified tissue effects after 1 year which were not seen after the final 2-year treatment no substance related effects were noted. From this 2-year feeding study a NOEL of 5.19 % Curry Red in the diet can be derived which is equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"%","noael_value":"5.19","page":7,"route":"oral","species":"dog","study_id":"out264_en_noael_004"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | =700 | mg/kg | dog | oral | - | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT== 700; DOSE=Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...; EFFECT=ndicate a weekly use of 35 ml for a semi-permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic poten; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","duration":"","effect":"ndicate a weekly use of 35 ml for a semi-permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic poten","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg","noael_value":"= 700","page":19,"route":"oral","species":"dog","study_id":"out264_en_noael_007"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | =700 | mg/kg | dog | oral | - | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT== 700; DOSE=Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...; EFFECT=permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic potential of Curry; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","duration":"","effect":"permanent hair dye, with a retention factor of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic potential of Curry","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg","noael_value":"= 700","page":19,"route":"oral","species":"dog","study_id":"out264_en_noael_008"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | =700 | mg/kg | dog | oral | - | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT== 700; DOSE=Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...; EFFECT=of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic potential of Curry Red after repeated application can be drawn; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 30...","duration":"","effect":"of 0.1. Absolute worst case calculation (assuming a daily use of 35 ml and a relative density of approximately 1.0 for the hair dye formulation) : Maximum absorption through the skin A (%) = 100 % Typical body weight of human = 60 kg Daily exposure to hair dye formulation = 35 g/day Retention Factor = 0.1 Concentration of dye in the formulation = 0.4 % Systemic exposure dose (SED) = 0.233 mg/kg/day No observed adverse effect level (mg/kg) NOAEL = 700 mg/kg Margin of Safety NOAEL / SED = 3000 2.12. Conclusions Toxicity Numerous oral toxicity studies administering Curry Red via gavage, drinking water or feeding to different species and for different treatment lengths are reported in the literature. The data package also covers long-term toxicity studies in two different rodent species and in dogs. Although the studies do not fulfil the current OECD, EU or EPA guidelines, a scientifically sound evaluation of the systemic toxic potential of Curry Red after repeated application can be drawn","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg","noael_value":"= 700","page":19,"route":"oral","species":"dog","study_id":"out264_en_noael_009"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | 700 | mg/kg bw/day | - | oral | - | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=700; DOSE=The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.; EFFECT=this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","duration":"","effect":"this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"700","page":19,"route":"oral","species":"","study_id":"out264_en_noael_013"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | - | 700 | mg/kg | - | - | - | - | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=700; DOSE=No observed adverse effect level (mg/kg) | NOAEL | 700 mg/kg; EFFECT=CALCULATION OF THE MARGIN OF SAFETY: No observed adverse effect level (mg/kg) | NOAEL | 700 mg/kg; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"No observed adverse effect level (mg/kg) | NOAEL | 700 mg/kg","duration":"","effect":"CALCULATION OF THE MARGIN OF SAFETY: No observed adverse effect level (mg/kg) | NOAEL | 700 mg/kg","endpoint":"","ingredient":"codes","loael_value":"","noael_unit":"mg/kg","noael_value":"700","page":19,"route":"","species":"","study_id":"out264_en_noael_014"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | carcinogenicity | 1.39 | % | - | oral | - | carcinogenicity | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=1.39; DOSE=In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species.; EFFECT=ng together all available data obtained with different species under different exposure scenarios. In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species.","duration":"","effect":"ng together all available data obtained with different species under different exposure scenarios. In summary, toxic effects were only noted, if at all, at high doses (> 1000 mg/kg bw/day) independent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw","endpoint":"carcinogenicity","ingredient":"codes","loael_value":"","noael_unit":"%","noael_value":"1.39","page":19,"route":"oral","species":"","study_id":"out264_en_noael_010"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | carcinogenicity | 7 | mg/kg bw/day | - | oral | - | carcinogenicity | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=7; DOSE=The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.; EFFECT=endent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","duration":"","effect":"endent of the exposure duration and species. No specific target organ for the systemic toxicity of Curry Red was found in rodents or any other species. In none of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in","endpoint":"carcinogenicity","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"7","page":19,"route":"oral","species":"","study_id":"out264_en_noael_011"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | carcinogenicity | 1.39 | % | - | oral | - | carcinogenicity | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=1.39; DOSE=The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.; EFFECT=e of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.; CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound.","duration":"","effect":"e of the combined long term toxicity/carcinogenicity studies in two rodent species any indication was found, for Curry Red being carcinogenic. Based on this finding, a NOEL of 1.39 % Curry Red in the diet, was deduced from this study by the study authors. Based on the available information, the study is considered to be scientifically valid and suitable for a NOEL deduction for a repeated exposure scenario. The SCF and the JECFA also used this study to derive an ADI of 7 mg/kg bw/day for this compound. The derived NOEL would be based on the mid dose male group receiving 1.39 % Curry Red in the diet and being equivalent to 701 mg/kg bw/day. Thus the corresponding NOAEL of 700 mg/kg bw/day can be used as the reference figure for the final risk assessment according to the SCCNFP-guidelines. However, it should be noted that compared to the expected frequency via application in hair colorants, the exposure duration in this study clearly represents a worst case scenario.","endpoint":"carcinogenicity","ingredient":"codes","loael_value":"","noael_unit":"%","noael_value":"1.39","page":19,"route":"oral","species":"","study_id":"out264_en_noael_012"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | developmental toxicity | 1000 | mg/kg bw/day | rat | - | prenatal | developmental toxicity | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=1000; DOSE=In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic.; EFFECT=of these variations were therefore considered to be accidental, moreover as they were within the historical controls range. In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic. Neither in the dams nor in the foetuses indications were noted for treatment-related adverse effects. Thus, for both the maternal and developmental toxicity a NOEL of ≥ 1000 mg/kg bw/day can be deduced from this study. Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited. Based on this information Curry Red is not a teratogen in rabbits (cited in reference 5) and no embryo-, foetotoxic or teratogenic effects were noted in rats treated during pregnancy with up to 200 mg/kg bw/day; highest dose tested in this test (cited in reference 2). Furthermore, the findings of a 2-generation study in rats are summarised in the mentio; CITATION=Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited; CITATION_NUMBERS=[10]; REFERENCE=Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited; DETAILS_JSON={"cas_number":"25956-17-6","citation":"Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited","dose":"In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic.","duration":"prenatal","effect":"of these variations were therefore considered to be accidental, moreover as they were within the historical controls range. In summary, the prenatal developmental toxicity study in Osborn Mendel rats investigating doses up to the limit dose of 1000 mg/kg bw Curry Red, did not reveal any indication for the test item to be embryo- or foetotoxic or teratogenic. Neither in the dams nor in the foetuses indications were noted for treatment-related adverse effects. Thus, for both the maternal and developmental toxicity a NOEL of ≥ 1000 mg/kg bw/day can be deduced from this study. Ref.: 10 In the literature, there are additional prenatal developmental studies in rats and rabbits cited. Based on this information Curry Red is not a teratogen in rabbits (cited in reference 5) and no embryo-, foetotoxic or teratogenic effects were noted in rats treated during pregnancy with up to 200 mg/kg bw/day; highest dose tested in this test (cited in reference 2). Furthermore, the findings of a 2-generation study in rats are summarised in the mentio","endpoint":"developmental toxicity","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"1000","page":12,"route":"","species":"rat","study_id":"out264_en_noael_006"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | repeated dose toxicity | 50 | mg/kg bw/day | rat | oral | 6-week | repeated dose toxicity | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=50; DOSE=Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.:; EFFECT=2, 3). 2.3. Toxicity 2.3.1. Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.: 2 2.3.2. Acute dermal toxicity No data 2.3.3. Acute inhalation toxicity No data 2.3.4. Repeated dose oral toxicity Mouse In a 6-week drinking water study groups of six male per group received doses of 0, 0.05 and 0.25 mg/ml Curry Red respectively in the drinking water. Bodyweight, drinking water consumption and investigations of brain, kidney, liver and spleen revealed no substance-related effects. A NOEL of 0.25 mg/ml in drinking water (equal to about 50 mg/kg bw/day, assuming a bodyweight of 25 g and a drinking water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals abou; CITATION=Ref.: 2 2; CITATION_NUMBERS=[2]; REFERENCE=Ref.: 2 2; DETAILS_JSON={"cas_number":"25956-17-6","citation":"Ref.: 2 2","dose":"Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.:","duration":"6-week","effect":"2, 3). 2.3. Toxicity 2.3.1. Acute oral toxicity Rat LD50 > 10000 mg/kg bw Dog LD50 > 5000 mg/kg bw Ref.: 2 2.3.2. Acute dermal toxicity No data 2.3.3. Acute inhalation toxicity No data 2.3.4. Repeated dose oral toxicity Mouse In a 6-week drinking water study groups of six male per group received doses of 0, 0.05 and 0.25 mg/ml Curry Red respectively in the drinking water. Bodyweight, drinking water consumption and investigations of brain, kidney, liver and spleen revealed no substance-related effects. A NOEL of 0.25 mg/ml in drinking water (equal to about 50 mg/kg bw/day, assuming a bodyweight of 25 g and a drinking water consumption of about 5 ml/day) can be derived from this study. Ref.: 2 Rat Groups of 6 male rats were fed 0 or 5.0 % Curry Red in a standard and a specially purified diet for 7 or 14 days. No effects on weight development were noted for the standard diet, whereas a slight reduction of bodyweight was noted for the purified diet. Based on this study administering 5 % Curry Red in the diet (equals abou","endpoint":"repeated dose toxicity","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"50","page":6,"route":"oral","species":"rat","study_id":"out264_en_noael_001"} |
| UnifiedCodex:SCCNFP:beta.noael_studies | repeated dose toxicity | 1500 | mg/kg bw/day | pig | oral | 21 days | repeated dose toxicity | SOURCE_SUBDIR=out264_en; REPORT_TITLE=OPINION OF THE SCIENTIFIC COMMITTEE ON COSMETIC PRODUCTS AND NON-FOOD PRODUCTS INTENDED FOR CONSUMERS CONCERNING CURRY RED COLIPA n° C174; OPINION_NUMBER=SCCNFP/0791/04; COMMITTEE=SCCNFP; REPORT_DATE=adopted by the SCCNFP on 23 April 2004; VALUE_TEXT=1500; DOSE=s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).; EFFECT=s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance related effects. For the described exposure scenario a NOAEL in pigs of 1500 mg/kg bw/day can be assumed. 2.3.5 Repeated dose dermal toxicity No data 2.3.6. Repeated dose inhalation toxicity No data 2.3.7. Subchronic oral toxicity See 2.3.4 2.3.8. Sub-chronic dermal toxicity No data 2.3.9. Sub-chronic inhalation toxicity No data 2.3.10. Chronic toxicity See also point 2.9. (combination studies chronic toxicity/carcinogenicity); CITATION_NUMBERS=[]; DETAILS_JSON={"cas_number":"25956-17-6","citation":"","dose":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg).","duration":"21 days","effect":"s equal to about 1500 mg/kg bw/day (assuming a feed consumption of 250 g/day and an average bodyweight of 8-9 kg). Pig Pigs (number of animals not indicated) were treated with Curry Red at an oral dose of 1000 mg/kg bw/day for 21 days followed by a dose of 1500 mg/kg bw/day until necropsy at day 76 (11 w). No effects were noted with regard to organ weights of liver, kidney and spleen. Haematology, clinical chemistry and histology did not reveal any substance related effects. For the described exposure scenario a NOAEL in pigs of 1500 mg/kg bw/day can be assumed. 2.3.5 Repeated dose dermal toxicity No data 2.3.6. Repeated dose inhalation toxicity No data 2.3.7. Subchronic oral toxicity See 2.3.4 2.3.8. Sub-chronic dermal toxicity No data 2.3.9. Sub-chronic inhalation toxicity No data 2.3.10. Chronic toxicity See also point 2.9. (combination studies chronic toxicity/carcinogenicity)","endpoint":"repeated dose toxicity","ingredient":"codes","loael_value":"","noael_unit":"mg/kg bw/day","noael_value":"1500","page":7,"route":"oral","species":"pig","study_id":"out264_en_noael_005"} |
openFDA substances 4 endpoints
| Source | Endpoint Type | Value | Unit | Species | Route | Duration | Study Type | Reference |
|---|---|---|---|---|---|---|---|---|
| openFDA substances | FDA UNII substance identifier | WZB9127XOA | UNII | - | - | - | chemical | {"approval_status":null,"molecular_formula":"C18H14N2O8S2.2Na","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"WZB9127XOA"} |
| openFDA substances | FDA UNII substance identifier | WZB9127XOA | UNII | - | - | - | chemical | {"approval_status":null,"molecular_formula":"C18H14N2O8S2.2Na","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"WZB9127XOA"} |
| openFDA substances | FDA UNII substance identifier | WZB9127XOA | UNII | - | - | - | chemical | {"approval_status":null,"molecular_formula":"C18H14N2O8S2.2Na","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"WZB9127XOA"} |
| openFDA substances | FDA UNII substance identifier | WZB9127XOA | UNII | - | - | - | chemical | {"approval_status":null,"molecular_formula":"C18H14N2O8S2.2Na","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"WZB9127XOA"} |