Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 701-417-7 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Description of key information
It is concluded that the pigment was well tolerated and that no signs of systemic toxicity whatsoever were observed in rats when administered at a dose of 1000 mg/kg bw/day for up to 28 days. The uptake of tin and chromium during a 24 hour urine and plasma sampling period was demonstrated to be negligible considering that <<0.05% of the dose was excreted via urine for both metals, mirrored by either minimal or no increases in blood plasma concentrations. This supports the assumption that both elements are not biologically available upon ingestion of the pigment chromium tin calcium silicon sphene. The no observed adverse effect level (NOAEL) in rats is 1000 mg/kg/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2015-07-24 to 2015-08-21
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Version / remarks:
- 2008-10-03
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- signed 2014-05-14
- Limit test:
- yes
- Specific details on test material used for the study:
- STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: at room temperature, kept dry and stored in a tightly closed container - Species:
- rat
- Strain:
- other: Crl:CD(SD)
- Details on species / strain selection:
- Rats were selected because of their proven suitability in toxicology studies and to comply with regulatory requirements for testing in a rodent animal species.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories Germany GmbH, Sandhofer Weg 7, 97633 Sulzfeld, Germany
- Age at study initiation: males: 57 days; females: 64 days
- Weight at study initiation: males: 294.5 g- 331.2 g; females: 230.0 g- 264.8 g
- Housing: animals were kept singly in MAKROLON cages (type III plus) with a basal surface of approx. 39 x 23 cm and a height of approx. 18 cm. Bedding material: granulated textured wood (Granulat A2, J. Brandenburg, 49424 Goldenstedt, Germany)
- Diet (ad libitum): Commercial ssniff® R/M-H V1530 diet (ssniff Spezialdiäten GmbH, 59494 Soest, Germany)
- Water (ad libitum): tap water
- Acclimation period: 9 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 °C ± 3 °C (maximum range)
- Humidity: 55 % ± 15 % (maximum range)
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Details on route of administration:
- The route of administration was selected according to the expected route of exposure.
- Vehicle:
- other: 0.5 % aqueous hydroxyl prpyl methylcellulose gel
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test item was suspended in the vehicle to the appropriate concentration. The administration formulation was continuously agitated by stirring throughout the entire administration procedure. The administration formulation was freshly prepared every day.
Administration volume: 10 mL/kg b.w./day. The amount of the test item was adjusted to each animal's current body weight daily.
VEHICLE
- Source: Fagron GmbH & Co. KG, 22885 Barybüttel, Germany
- Batch no.:13DO3-NO3 - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- For each test item that was mixed with a vehicle, tests by appropriate analytical methods were conducted to determine the concentration, stability and homogeneity of the test item in the formulations. For the analysis of the test item-vehicle mixtures, samples of approximately 10 mL were taken at the following times and stored at ≤-20°C until dispatch:
1) At study initiation:
- analysis of stability and concentration: Immediately after preparation of the administration formulation as well as after 8 and 24 hours storage at room temperature (number of samples: 3).
- homogeneity: At the start of administration, during (middle) administration and before administration to the last animal of group 2 (number of samples: 3).
2) at study termination:
- analysis of concentration: During treatment always before administration to the last animal of group 2 (number of samples: 1- sum of all samples: 7).
The samples were prepared for digestion and then the digested samples were measured by ICP-OES and ICP-MS.
Before total digestion and measurement of total chromium and tin in the application solutions the samples were retrieved from the cryogenic storage container and thawed at least overnight. Afterwards, the total amount of each application solution was transferred into a 50 mL centrifugation vial and concentrated nitric acid was added. After shaking for 72 h the samples were centrifuged to speed-up the sedimentation of the pigment (15 minutes at 4500
rpm, Allegra X-15R). Therefore, centrifugation time and speed were determined as required. Subsequently, as much supernatant as possible (without taking up pigment) was transferred into a 50 mL vial and filled up with ultra-pure water to 50 mL, and measured by ICP-MS and ICP-OES. Furthermore, concentrated HNO3 was added to each empty original application solution vial, which were also shaken for 72 hours. The nitric acid was also measured by ICP-OES and ICP-MS. This procedure was performed for each application solution.
After the remove of the supernatant the remaining pigment was shared into three digestion vials. 5 mL concentrated HNO3 were filled in each digestion vial and the samples were digested by a microwave procedure (UltraClave II and UltraClave V). After digestion in all three subsamples as much supernatant as possible without transfer of pigment was removed by a pipette and combined in a 15 mL vial and was filled up exactly to 15 mL. After the first digestion ten further digestions were performed. Therefore, the remaining pigment was filled up with the respective digestion medium. Besides 69 % HNO3, mixtures of HNO3/H2O2 or HNO3/HF were used as digestion medium; also different microwave programmes were applied. The supernatants of each digestion were measured by ICP-OES. After the 11th digestion, the procedure was aborted as it turned out to be too time-consuming and not promising. Subsequently, the remaining pigment was lyophilised and the residual amount of pigment determined gravimetrically.
The ICP-OES measurements were performed with an Agilent 720 ICP-OES and an Agilent 5110 VDS ICP-OES. The following solutions were used to calibrate the instrument (not all calibration solutions were used in each measurement series): blank, 1.0 μg/L, 2.0 μg/L, 2.5 μg/L, 4.0 μg/L, 5.0 μg/L, 6.0 μg/L, 7.5 μg/L, 8.0 μg/L, 10.0 μg/L, 20 μg/L, 25 μg/L, 40 μg/L, 50μg/L, 60 μg/L, 75 μg/L, 80 μg/L, 100 μg/L, 200 μg/L, 250 μg/L, 400 μg/L, 500 μg/L, 600 μg/L, 750 μg/L, 800 μg/L, 1000 μg/L, 2000 μg/L, 4000 μg/L and 6000 μg/L.
Calibrations were performed before each measurement and in the respective acid matrix (matrix adaption of calibration solution). The linearity of the calibration was adequate for the lower and higher concentration range. In some measurement series, individual concentrations were excluded from the calibration by the instrument software since the nominal concentration was ± 25% of the measured concentration, i.e. mainly low concentrations for which the difference between background of blank and concentration was not high enough. The calibration formula was calculated using the linear regression algorithm
of the ICP-OES instrument. The correlation coefficients (r) for the wavelengths used for evaluation of data were at least 0.9998 (required 0.995). Specific wavelengths for the data evaluation were selected based on the best recovery of chromium and tin in quality control samples (certified waters, recovery/fortification samples, etc.). Furthermore, the wavelengths were checked for possible interferences and wavelengths with a possible interference were
not taken into account for a possible evaluation.
Instrumental and analytical set-up for the ICP-OES instruments:
Instrument: Agilent 720, Agilent Technologies, Waldbronn, Germany
Nebulizer: Sea spray nebulizer, from Glass Expansion
Spray chamber: Iso Mist with Twister Helix from Glass Expansion
Plasma stabilization time: at least 30 min before start of the measurements
Plasma gas flow: 15.0 L/min
Additional gas flow: 1.50 L/min
Carrier gas flow: 0.75 L/min
RF power: 1200W
Stabilization time of sample: 15 sec
Repetition time: 30 sec (three internal measurements per sample)
Wavelengths: Cr: 205.560 nm, 267.716 nm, 283.563 nm, 284.984 nm,
285.567 nm and 357.868 nm
Sn: 183.113 nm, 189.925 nm, 215.152 nm, 226.893 nm, 235.485 nm, 242.950 nm, 283.998 nm and 326.233 nm
Instrument: Agilent 5110 VDS, Agilent Technologies, Waldbronn, Germany
Nebulizer: Sea spray nebulizer, from Glass Expansion
Spray chamber: Iso Mist with Twister Helix from Glass Expansion
Plasma stabilization time: at least 30 min before start of the measurements
Plasma gas flow: 12.0 L/min
Additional gas flow: 1.0 L/min
Carrier gas flow: 0.7 L/min
RF power: 1200 W
Stabilization time of sample: 20 sec
Repetition time: 30 sec (three internal measurements per sample)
Wavelengths: Cr: 205.560 nm, 206.158 nm, 206.550 nm, 267.716 nm,
283.563 nm
Sn: 181.059 nm, 189.925 nm, 235.485 nm, 242.950 nm and 283.998 nm
At least three internal measurements for each sample were performed and the mean was calculated and printed by the instrument software.
The applied LOD/LOQ calculations are (according to DIN 32645) (Chemische Analytik - Nachweis-, Erfassungs- und Bestimmungsgrenze unter Wiederholbedingungen – Begriffe, Verfahren, Auswertung; German version DIN 32645:2008-11. Beuth Verlag.):
LOD: 3 × standard deviation of calibration blank/slope of the calibration
LOQ: 3 × LOD
The resulting LODs/LOQs are as follows:
- LOD: 0.106 - 0.646 µg/L (Cr); 0.729 - 19.2 µg/L (Sn)
- LOQ: 0.318 - 1.94 µg/L (Cr); 2.19 - 57.5 µg/L (Sn)
- correlation coefficient: 0.9998 - 1.00000 (Cr); 0.9998 - 1.00000 (Sn)
Certified reference materials as well as quality control standards, recalibration standards and fortification samples (recovery samples) were analysed as quality assurance samples along with the test samples during the measurement. To meet quality assurance requirements recovery needs to be in the range of ± 15 % of the respective certified value or the nominal/calculated values. Since possible interferences of the quality control samples could not be excluded during a measurement series at least 60% of the quality assurance samples
have to be valid (according to internal laboratory SOPs). Under specific circumstances, this 60% can also be lowered if specific interferences can be proved for example influence of elements in one specific reference material due to concentration interference.
Results:
Results:
Analysis of stability and concentration (3 samples):
Recovery [%]:
Cr:. 20.6 - 24.8
Sn: 13.4 - 15.8
Anaylsis of homogenity (3 samples):
Recovery [%]:
Cr:. 21.9 - 26.1
Sn: 11.8 - 21.8
Anaylsis of concentration (1 sample):
Recovery [%]:
Cr:. 24.9
Sn: 16.7 - Duration of treatment / exposure:
- 28 days
- Frequency of treatment:
- once daily
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 5 males/ 5 females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: in agreement with the Sponsor and based on available toxicity data a limit test was performed.
- Positive control:
- none
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule (clinical signs): before and after dosing at each time of dosing as well as regularly throughout the working day from 7:30 a.m. to 4.30 p.m. and on Saturdays and Sundays from 8.00 a.m. to 12.00 noon with a final check performed at approximately 4.00 p.m.
- Time schedule (mortality): early in the morning and again in the afternoon of each working day as well as on Saturdays and Sundays with a final check at approximately 4.00 p.m.
- Cage side observations checked: clinical signs and mortality
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once before the first exposure and once a week thereafter (1, 2, 4, 8 and 24 hours after administration) as well as in the test week 4 prior to any laboratory investigations.
BODY WEIGHT: Yes
- Time schedule for examinations: at the time of group allocation, on the day of commencement of treatment and once a week thereafter, always on the same day of the week
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
The quantity of food left by individual animals was recorded on a weekly basis throughout the experimental period. Food intake per rat (g/rat/week) was calculated using the total amount of food given to and left by each rat in each group on completion of a treatment week.
The relative food consumption (in g/kg b.w./day) was determined.
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No
WATER CONSUMPTION AND COMPOUND INTAKE: Yes
- Time schedule for examinations: daily
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: prior to the start of administration and at the end of test week 4.
- Dose groups that were examined: all animals
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at study termination (on the day of dissection)
- Anaesthetic used for blood collection: Yes, isoflurane anaesthesia
- Animals fasted: Yes , overnight
- How many animals: all animals
- Parameters examined: haemoglobin content, erythrocytes, leucocytes, retriculocytes, platelets, haematocrit value, differential blood count (relative and absolute- neutrophilic, eosinophilic and basophilic granulocytes, lymphocytes and monocytes), mean corpuscular haemoglobin, mean corpuscular haemoglobin concentration, mean corpuscular volume, prothrombin time, activated partical thromboplastin time
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood:
- Animals fasted: Yes, overnight
- How many animals: all animals
- Parameters examined: albumin, globulin, albumin/globulin ratio, bile acids (total), bilirubin (total), cholesterol (total), creatinine, glucose, protein (total), urea (in blood), calcium, chloride, potassium, sodium, alanine amino-transferase, alkaline phosphatase, aspartate aminotransferase, lactate dehydrogenase
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations: in test week 4 approx. 1 to 2 hours after dosing and before any blood sampling
- Dose groups that were examined: all animals
- Battery of functions tested: sensory activity / grip strength / motor activity
1) Observational screening: righting reflex, body temperature, salivation, startle response, respiration, mouth breathing, urination, convulsions, pilo-erection, diarrhoea, pupil size, pupil response, lacrimation, impaired gait, stereotypy, toe pinch, tail pinch, wire manoeuvre, hind-leg splay, positional passivity, tremors, positive geotropism, limb rotation, auditory function
2) Functional tests: grip strength and locomotor activity
IMMUNOLOGY: No
OTHER:
TOXICOKINETICS: Yes (please refer to Fraunhofer IME, report no. EBR-213/6-27)
Urine and plasma samples were obtained at study termination for the determination of the chrome and tin levels by ICP-OES and ICP-MS.
- urine sample: individual urine samples were collected from all animals for a 24-hour period following the last administration on test day 28 (one 24-hour fraction/animal). For this purpose, the animals were placed in metabolic cages during the 24-hour collection period, directly after the last oral administration.
- plasma sample: 24 hours after the last administration, a terminal blood sample was collected from all animals by puncture from the retrobulbar venous plexus under isoflurane anaesthesia in order to obtain 0.5 mL LiHeparin plasma/animal. Afterwards, the animals were sacrificed and dissected - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes
On test day 29 (approximately one day after the last administration), the animals were dissected following a randomisation scheme. The animals were sacrificed by carbon dioxide (CO2) inhalation, exsanguinated by cutting the aorta abdominalis, weighed, dissected and inspected macroscopically under the direction of a pathologist. All superficial tissues were examined visually and by palpation and the cranial roof was removed to allow observation of the brain, pituitary gland and cranial nerves. After ventral midline incision and skin reflection all subcutaneous tissues were examined. The condition of the thoracic viscera was noted with due attention to the thymus, lymph nodes and heart. The abdominal viscera were examined before and after removal, the urinary bladder was examined externally and by palpation. The gastro-intestinal tract was examined as a whole and the stomach and caecum were incised and examined. The lungs were removed and all pleural surfaces examined under suitable illumination. The liver and the kidneys were examined. Any abnormalities in the appearance and size of the gonads, adrenal glands, uterus, intra-abdominal lymph nodes and accessory reproductive organs were recorded. The weights of the following organs of all animals were determined before fixation: Adrenal gland (2), Brain, Epididymis (2), Heart, Kidney (2), Liver, Ovary (2), Spleen, Testicle (2), Thymus, As a whole: Prostate and seminal vesicles with coagulating glands. Paired organs were weighed individually and identified as left or right.
The following organs or parts of organs of all animals were fixed in 7% buffered formalin. The eyes were fixed in Davidson's solution and the testes in Bouin's solution for optimum fixation:
Adrenal gland (2), Bone (os femoris with joint), Bone marrow (os femoris) Brain (3 levels: cerebrum, cerebellum, medulla/pons), Epididymis (2), Eye with optic nerve (2), Gross lesions observed, Heart (3 levels: right and left ventricle, septum), Intestine, large (colon, rectum), Intestine, small (duodenum, jejunum, ileum, incl. Peyer's patches), Swiss roll method, Kidney and ureter (2), Liver, Lungs (with mainstem bronchi and bronchioles (preserved by inflation with fixative and then immersion)), Lymph node (1, cervical), Lymph node (1, mesenteric), Mammary gland, Muscle (skeletal, leg), Nerve (sciatic), Ovary (2), Pituitary, Prostate and seminal vesicles with coagulating glands, Spinal cord (3 sections), Spleen, Stomach, Testicle (2), Thymus, Thyroid (2) (incl. parathyroids), Tissue masses or tumours (incl. regional lymph nodes), Trachea (incl. larynx), Urinary bladder, Uterus (incl. cervix and oviducts), Vagina
The above-listed organs of all animals were examined histologically after preparation of paraffin sections and haematoxylin-eosin staining. In addition, frozen sections of the heart, liver and one kidney were made, stained with Oil Red O and examined microscopically. Parathyroids cannot always be identified macroscopically. They were examined microscopically if in the plane of section and in all cases where they were noted as grossly enlarged. - Statistics:
- The test item-treated Group 2 was compared with the control Group 1.
The following statistical methods were used:
1) STUDENT's t-test All numerical functional tests / Body weight / Food consumption / Haematology and coagulation / Clinical biochemistry / Relative and absolute organ weights (p ≤ 0.05 and p ≤ 0.01)
The following limits were used:
p = 0.05/0.01 ^ t = 2.3060/3.3554 (for 8 degrees of freedom)
2) Exact test of R. A. FISHER Histology (p ≤ 0.05 and p ≤ 0.01) - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
- Details on results:
- CLINICAL SIGNS:
- No adverse changes in behaviour, external appearance or faeces were noted for the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day or for the animals treated with the vehicle control once daily for 28 days.
- all male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day revealed purple discoloured faeces as of test day 3. This finding is considered to be due to the test item per se being a pink powder and, hence, is not an adverse effect.
MORTALITY:
- None of the animals died prematurely during the study
BODY WEIGHT AND WEIGHT CHANGES
- No test item-related influence was observed for the body weight, the body weight gain and body weight at autopsy in the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28 days. All data are regarded to be within the normal range.
FOOD CONSUMPTION AND COMPOUND INTAKE
- No test item-related changes in relative food consumption were noted for the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28 days compared to the control group.
WATER CONSUMPTION AND COMPOUND INTAKE
- The visual appraisal of the drinking water consumption did not reveal any test item related influence.
OPTHALMOLOGICAL FINDINGS
- Ophthalmological examination revealed no changes of the eyes and the optic region in the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day or for the animals treated with the vehicle control once daily for 28 days.
HAEMATOLOGICAL FINDINGS
- No test item-related influence in haematological and coagulation parameters was noted for the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28 days compared to the control group.
CLINICAL BIOCHEMISRY FINDINGS
- No test item-related influence in biochemical parameters was noted for the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28 days compared to the control group.
- Statistically significant differences in biochemical parameters compared to the control which are not considered to be test item-related: males (test day 29): decreased cholesterol; males (test day 29): decreased calcium
BEHAVIOUR (FUNCTIONAL FINDINGS)
- The neurological screening performed at the end of the treatment period in test week 4 approximately 1 to 2 hours after dosing did not reveal any test item-related influence in the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28 days, neither on any of the parameters examined during the functional observation tests nor on the fore- and hind limb grip strength or on the spontaneous motility. The examination results of the animals treated with the vehicle control were also in the normal range.
ORGAN WEIGHT FINDINGS INCLUDING ORGAN/BODY WEIGHT RATIOS
- No test item-related changes in relative and absolute organ weights were noted for the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28-days compared to the control group.
GROSS PATHOLOGICAL FINDINGS
- None of the male and female rats treated with 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day once daily for 28-days revealed any macroscopic changes at necropsy on test day 29.
HISTOPATHOLOGICAL FINDINGS: NON-NEOPLASTIC
- The histomorphological examination did not reveal any morphological changes which are considered to be related to the administration of the test item. There was no difference between the groups.
- The inflammatory lesions in different organs are considered to be coincidental findings or spontaneous organ changes and are thus not test item-related. No differences were noted between the groups.
- The fatty infiltration in the hepatocytes and in the tubular epithelial cells of the kidney in male and female rats of the control and/or the test item-treated group were within the physiological limits.
- The involution of the thymus in the rats of both groups corresponded in type, incidence and severity to the age of the animals.
- The coincidental findings from different organs in a small number of control and test item-treated animals are considered to be spontaneous organ changes and are thus not test item-related.
- No morphological differences were noted for any of the organs examined between the controls and the high dose group 2. Type, incidence and severity of the lesions were comparable to the control animals.
OTHER
TOXICOKINETICS
The uptake of tin and chromium during a 24 hour urine and plasma sampling period was demonstrated to be negligible considering that <<0.05% of the dose was excreted via urine for both metals, mirrored by either minimal or no increases in blood plasma concentrations. This supports the assumption that both elements are not biologically available upon ingestion of the pigment chromium tin calcium silicon sphene.
Please also refer to the field "Attached background material" below. - Key result
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Critical effects observed:
- no
- Conclusions:
- NOAEL (oral; rats) > 1000 mg Chromium tin calcium silicon sphene (Pigment red 233)/kg b.w./day
No test item-related changes were observed for clinical signs, mortality, neurologically screening, body weight/body weight gain, food consumption, water consumption, haematology, clinical chemistry, organ weights, ophthalmology, gross pathology, and histopathology.
The uptake of tin and chromium during a 24 hour urine and plasma sampling period was demonstrated to be negligible considering that <<0.05% of the dose was excreted via urine for both metals, mirrored by either minimal or no increases in blood plasma concentrations. This supports the assumption that both elements are not biologically available upon ingestion of the pigment chromium tin calcium silicon sphene.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Animal data – oral route
A 28-day repeated dose toxicity limit test in rats was conducted (LPT, 2021) to assess the effect of the pigment on rats following repeated oral administration. The study was conducted according to OECD test guideline 407, and in compliance with GLP. Male and female rats were administered with the pigment by oral gavage for 28 days at a dose of 1000 mg/kg bw/day in 0.5% aqueous hydroxyl propyl methylcellulose gel. A concurrent control group was administered untreated vehicle.
No clinical signs of toxicity were observed, and no animals died during the administration period. No changes in bodyweight gains, food/water consumption, haematology, clinical chemistry, organ weights or macropathology were observed which could be attributed to treatment with the test compound. The histomorphological examination of rat organs did not reveal any morphological lesions attributable to the administration of the test item. There were no morphological differences between the control rats and the test item-treated animals. No adverse effects were observed on the male and female reproductive organs.
Furthermore, individual 24-hour urine samples were collected from all animals after the last dosing prior to the scheduled sacrifice, and in addition plasma samples were collected from each animal at the day of sacrifice. The plasma and urine samples were analysed for total tin and chromium content. The tin and chromium concentrations of the 24 hour urine samples, collected during the day before sacrifice, ranged from 1.07 µg/mL for males and 1.30 µg/mL for females and 0.1 µg/L for males and of 35.4 µg/L for females,respectively. The tin and chromium concentrations of plasma samples, collected from dose group animals at the day of sacrifice, ranged from 0.038 µg/mL for males and 0.018 µg/mL for females and 0.228 µg/L for males and of 0.043 µg/L for females, respectively.
It is concluded that the pigment was well tolerated and that no signs of systemic toxicity whatsoever were observed in rats when administered at a dose of 1000 mg/kg bw/day for up to 28 days. The uptake of tin and chromium during a 24 hour urine and plasma sampling period was demonstrated to be negligible considering that <<0.05% of the dose was excreted via urine for both metals, mirrored by either minimal or no increases in blood plasma concentrations. This supports the assumption that both elements are not biologically available upon ingestion of the pigment Chromium tin calcium silicon sphene. The no observed adverse effect level (NOAEL) in rats is 1000 mg/kg/day.
Justification for classification or non-classification
No signs of systemic toxicity whatsoever were observed in rats when administered at a dose of 1000 mg/kg bw/day for up to 28 days. The no observed adverse effect level (NOAEL) in rats is 1000 mg/kg/day.
No classification for repeated dose toxocity according to EC Regulation No. 1272/2008 is anticipated.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.