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"}