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EC number: 231-912-9 | CAS number: 7778-74-7
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-guideline study
Data source
Reference
- Reference Type:
- publication
- Title:
- The Metabolism of Perchlorate in the Rat
- Author:
- Goldman SJ & Stanbury JB
- Year:
- 1 973
- Bibliographic source:
- Endocrinology 92: 1536
Materials and methods
- Objective of study:
- metabolism
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The disposal of potassium perchlorate was studied in rats maintained on low iodine diet.
- GLP compliance:
- no
Test material
- Reference substance name:
- Potassium perchlorate
- EC Number:
- 231-912-9
- EC Name:
- Potassium perchlorate
- Cas Number:
- 7778-74-7
- Molecular formula:
- ClHO4.K
- IUPAC Name:
- potassium perchlorate
- Test material form:
- not specified
- Details on test material:
- - Name of test material (as cited in study report):potassium perchlorate K36ClO2
- Molecular formula (if other than submission substance):K36ClO2
- Substance type:
- Physical state:
- Analytical purity: no data
- Purity test date: no data
- Lot/batch No.: no data
- Expiration date of the lot/batch: no data
- Radiochemical purity (if radiolabelling): no information
- Specific activity (if radiolabelling): 240µCi/mmole
- Locations of the label (if radiolabelling): 36Cl
- Expiration date of radiochemical substance (if radiolabelling): no data
- Stability under test conditions: stable for duration of the assay
- Storage condition of test material: no data
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- perchlorate labelled with 36Cl
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no data
- Age at study initiation: no information
- Weight at study initiation: Group 1 - 24 rats weighing between 200 and 250g. Group 2 - 20 rats weighing between 300 and 350g.
- Fasting period before study: Group 1 was maintained on low iodine diet for 5 weeks prior to first administration of potassium perchlorate. Group 2 was maintained on low iodine diet for 4.5 weeks prior to first administration of potassium perchlorate.
- Housing: No information
- Individual metabolism cages: no data
- Diet (e.g. ad libitum): Remington diet (low iodine), provided by General Biochemical Inc., Chagrin Falls, Ohio , available ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: circa 4-5 weeks on Remington diet before dosing initiated
ENVIRONMENTAL CONDITIONS
- Temperature (°C): no information
- Humidity (%): no information
- Air changes (per hr): no information
- Photoperiod (hrs dark / hrs light): no information
IN-LIFE DATES: From: no information To: no information
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- physiological saline
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: Radiolabelled potassium perchlorate with specific activity of 240 µCi/mmole prepared in 1 mL of saline solution and injected as a 0.1 µCi dose (approximately 40 µg of stable perchlorate per injection)
DIET PREPARATION
- Rate of preparation of diet (frequency):
- Mixing appropriate amounts with (Type of food):
- Storage temperature of food:
VEHICLE
- Justification for use and choice of vehicle (if other than water):
- Concentration in vehicle:
- Amount of vehicle (if gavage):
- Lot/batch no. (if required):
- Purity:
HOMOGENEITY AND STABILITY OF TEST MATERIAL: - Duration and frequency of treatment / exposure:
- In Group 1 the four subgroups were terminated 2, 8, 24 and 48 h after dosing.
In Group 2 three of the four subgroups were treated the same as Group 1 and then terminated 2, 8 or 24 h after dosing. The fourth subgroup was dosed at 0.2 µCi/mmole and terminated after 96 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0.1 µCi/mmole and 0.2 µCi/mmole
- No. of animals per sex per dose / concentration:
- Group 1 - 4 subgroups each consisting of six male rats
Group 2 - 4 subgroups each consisting of five male rats - Control animals:
- no
- Positive control reference chemical:
- No information
- Details on study design:
- - Dose selection rationale: perchlorate anions competitively inhibit uptake of iodine by the thyroid in both rats and humans; and discharge accumulated iodide not covalently bound in organic form. Perchlorate is selectively concentated by rats in the thyroid but undergoes no chemical change between injection and excretion and is therefore a good biological marker for thyroid uptake and tissue distribution models and selective uptake reduces the required concentration. Two dose levels, 0.1 and0.2 µCi/mmole, were selected.
- Details on dosing and sampling:
Tissue samples obtained from Group 2 subgroup 4 included thyroid, kidney, spleen, liver and brain.
Urine samples were collected over 24 hour intervals up to 96 hours after dosing (Group 2, subgroup 4)- Statistics:
- No data
Results and discussion
- Preliminary studies:
- No information
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- No information
- Details on distribution in tissues:
- No accumulation ofradionuclide in liver, brain, kidneys or spleen. Maximum concentration in thyroid was achieved afte 4 hours. Rates of disappearance from thyroid and plasma, and rate of appearance in urine, were exponential with a half-time of circa 20 hours.
- Details on excretion:
- Rates of disappearance from thyroid and plasma, and rate of appearance in urine, were exponential with a half-time of 20 hours.
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- No information
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- No data
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
Following intraperitoneal administration to rats, maximal thyroid concentration was attained approximately 4 hours after dosing. Maximum concentration was 2.5 % of the dose per g of tissue. All of th radionuclide in the thyroid was soluble in trichloracetc acid. No significant concentration of radionuclide was recovered from kidney, liver,spleen or brain tissue. The rate of disappearance from plasma or from thyroid and the rate of appearance in urine were all exponential, with half-times of circa 20 hours. These disposal rates were similar to rates calculated for radiolabelled iodide by other workers. - Executive summary:
The disposal of potassium perchlorate was studied in rats maintained on low iodine diet. Following intraperitoneal injection the radionuclide levels were monitored in the thyroid. Radionuclide levels were also monitored in kidney, liver, brain and spleen. Radionuclide disappearance rates from plasma and thyroid were measured together with the appearance rate in urine. Half life times were calculated for various rates.
Perchlorate displacement of iodide in rat thyroid has been widely used in therapeutic situations, blocking iodide entry into the thyroid or discharging previously accumulated, non-covalently bound iodide (e.g. in patients with Pendred's syndrome). The use of radiolabelled perchlorate in the current assay demonstated low levels of thyroid uptake at the specific activities used, no evidence of covalent binding of the radionuclide in the thyroid, no selective retention of the radionuclide in the examined tissues and exponential disappearance from the body with a half life of 20 hours.
The authors indicate that the current tests used the lowest radiolabelled perchorate dose consistent with adequate counting rates and the highest specific activities. Calculating radiation doses for administration to man by reference to the behaviour of
radiolabelled perchlorate appears reasonable based on the metabolic similarities to iodide and disposal and retention properties being similar to iodide when covalent binding of iodide is blocked.
Following intraperitoneal administration to rats, maximal thyroid concentration was attained approximately 4 hours after dosing. Maximum concentration was 2.5 % of the dose per g of tissue. All of th radionuclide in the thyroid was soluble in trichloracetc acid. No significant concentration of radionuclide was recovered from kidney, liver,spleen or brain tissue. The rate of disappearance from plasma or from thyroid and the rate of appearance in urine were all exponential, with half-times of circa 20 hours. These disposal rates were similar to rates calculated for radiolabelled iodide by other workers.
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