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EC number: 267-956-0 | CAS number: 67953-76-8
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1978-10-30 to 1980-11-04
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Reason / purpose for cross-reference:
- read-across source
- Type:
- distribution
- Results:
- small amount of test substance found in bones 0.033% in total skeleton; 0.0065% after test period
- Details on absorption:
- After 4 weeks 0.069 mg HEDP/kg bone (1.1 µg absolute) was found in the skeleton. This is equivalent to 0.033% of the substance administered. After 104 weeks, the amount in the skeleton was 0.0065% of the overall intake. As the radioactive levels of all organs and tissue samples with the exception of bone and intestine were only slightly above the limit of detection, the amount of HEPD absorbed from drinking water was apparently low.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 986
- Report date:
- 1986
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The study was conducted to determine the possible cumulative effects of ¹⁴C HEDP administered in drinking water over 2 years.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Sodium Salts of (1-Hydroxyethylidene)bisphosphonic acid (2-3 Na:1)
- EC Number:
- 701-238-4
- Molecular formula:
- HEDP-2Na C2H6Na2O7P2 HEDP-3Na C2H5Na3O7P2
- IUPAC Name:
- Sodium Salts of (1-Hydroxyethylidene)bisphosphonic acid (2-3 Na:1)
- Test material form:
- solid
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Winkelmann GmbH, BOrchen
- Age at study initiation: ca. 8 weeks
- Weight at study initiation: ca 200 g
- Fasting period before study: no
- Housing: Makrolon cages
- Individual metabolism cages: no 93 animals per cage)
- Diet: Altromin Haltungsdiät, ad libitum
- Water (e.g. ad libitum): test substance was administered in water, available ad libitum. Water consumption was measured in the first and second weeks, and then every two weeks, to obtain an average daily dose and a cumulative dose.
- Acclimation period: no information
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20°C (test animals) 21°C (control animals)
- Humidity (%): 50% (isotope lab, test animals) 60% (control animals)
- Air changes (per hr): no information
- Photoperiod (hrs dark / hrs light): natural daylight, therefore, variable.
IN-LIFE DATES: From: approx October 4th 1978 To: November 11th 1980
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Duration and frequency of treatment / exposure:
- Continuous via ad libitum drinking water over 2 years.
Doses / concentrations
- Dose / conc.:
- 134 mg/kg bw/day
- Remarks:
- equivalent to daily intake 0.184 mg/kg bw
- No. of animals per sex per dose / concentration:
- 150 male test animals, 75 controls
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Dose selection rationale: The dose used was chosen on the assumption that a certain amount (10%) can be swallowed by using a tooth-paste containing 0.5 -1% HEDP.
- Rationale for animal assignment (if not random): no information - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (distribution)
- Tissues and body fluids sampled: blood, tibia
- Time and frequency of sampling: every four weeks in four test animals and two control animals.
- Radioactivity of organs was determined after drying.
- X-rays were taken to determine distribution of radiation, and morphology of bones.
- Other: Test animals remaining after 106 weeks treatment were observed for another 33 weeks, and then killed. Necroscopies were carried out. - Statistics:
- t-test for water and food consumption, U-test for organ weight.
Results and discussion
Main ADME results
- Type:
- distribution
- Results:
- small amount of test substance found in bones 0.033% in total skeleton; 0.0065% after test period
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- After 4 weeks 0.069 mg HEDP/kg bone (1.1 µg absolute) was found in the skeleton. This is equivalent to 0.033% of the substance administered. After 104 weeks, the amount in the skeleton was 0.0065% of the overall intake. As the radioactive levels of all organs and tissue samples with the exception of bone and intestine were only slightly above the limit of detection, the amount of HEPD absorbed from drinking water was apparently low.
- Details on distribution in tissues:
- Very little radioactivity was detected anywhere except in the bones. About 95% of the absorbed HEDP was found in the skeleton and 3% in the liver.
Any other information on results incl. tables
X ray studies showed that there was no influence of HEDP on morphology and length of bones.
Food consumption and body weight increased slightly in comparison with the control group.
No treatment related effects were observed in the following evaluations:
macroscopical and microscopical examinations
blood chemistry (including determination of magnesium, iron and zinc in serum)
urinalysis
bone marrow smears
organ weight determination
determination of calcium and phosphor in trachaea and tibia
Table 1 Distribution of ¹⁴C after 2 year exposure to 3.3 ppm ¹⁴C-HEDP in drinking water
Organ |
¹⁴C-activity in % overall intake |
¹⁴C-activity, relative distribution (%) |
Intestine |
5.7 ± 5.4 x 10ˉ³ |
40.70 |
Bones |
7.6 ± 1.2 x 10ˉ³ |
54.30 |
Thyroid gland |
1.3 ± 0.2 x 10ˉ⁵ |
0.09 |
Stomach |
1.0 ± 0.7 x 10ˉ⁴ |
0.71 |
Bladder |
4.2 ± 1.2 x 10ˉ⁵ |
0.30 |
Liver |
2.6 ± 1.1 x 10ˉ⁴ |
1.86 |
Lungs |
2.1 ± 0.5 x 10ˉ⁵ |
0.15 |
Tongue |
4.7 ± 4.7 x 10ˉ⁶ |
0.03 |
Kidneys |
3.1 ± 0.1 x 10ˉ⁵ |
0.22 |
Testicles |
4.0 ± 1.7 x 10ˉ⁵ |
0.28 |
Eyes |
2.8 ± 1.9 x 10ˉ⁶ |
0.02 |
Muscles |
2.2 ± 0.5 x 10ˉ⁵* |
- |
Spleen |
6.6 ± 0.9 x 10ˉ⁶ |
0.05 |
Pancreas |
2.3 ± 0.8 x 10ˉ⁵ |
0.16 |
Brain |
1.0 ± 0.6 x 10ˉ⁵ |
0.07 |
Heart |
5.6 ± 1.9 x 10ˉ⁶ |
0.04 |
Skin |
1.7 ± 1.3 x 10ˉ⁵* |
- |
Sum without stomach and intestine |
8.0 ± 1.1 x 10ˉ³ |
- |
Total sum |
1.4 ± 0.7 x 10ˉ² |
98.9 |
* Tissue weight not known
Applicant's summary and conclusion
- Conclusions:
- In an in vivo basic toxicokinetic study, not conducted according to any OECD Test Guideline and unknown if in compliance with GLP, rats were exposed to a continuous oral intake of radio-labelled HEDP (2-2Na) in drinking water at concentrations of 134 mg/kg bw/day over a two-year period. During the test period, the amount of HEDP was 0.033 % in the total skeleton, however, by the end of the test period the proportion was 0.0065 %. The absorption in bones was approximately 0.0065% of the amount of substance consumed. It is concluded that a small proportion of HEDP administered in drinking water is absorbed from the intestinal tract and reaches the bones. The amount in the skeleton decreases after administration ceases.
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