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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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- No data
- 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:
- developmental toxicity
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- See read-across justification in IUCLID Section 13
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 100 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: No adverse effects observed
- Remarks on result:
- other: equivalent to 82.4 mg/kg bw/day
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- ca. 447 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: No adverse effects observed
- Remarks on result:
- other: equivalent to 368 mg/kg bw/day active acid
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 100 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No adverse effects
- Remarks on result:
- other: equivalent to 82.4 mg/kg bw/day
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 447 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: No adverse effects
- Remarks on result:
- other: equivalent to 0.5% in diet and 368 mg/kg bw/day active acid
- Key result
- Developmental effects observed:
- no
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 971
- Report date:
- 1970
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- Dosing from day 2-16 instead of day 6-18; uterine weights (does) and sex ratios (offspring) were not evaluated
- GLP compliance:
- no
- Remarks:
- prior to GLP
- Limit test:
- no
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:
- not specified
1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS:
Virgin New Zealand rabbits, 5-6 months of age and about 4 kg bodyweight at the time of insemination, were randomly distributed into groups of 25 (pre-study) or 20 (main study) does on the basis of weight and litter after an 18-day holding period. Water and food (Purina Rabbit Chow) was available ad libitum. They were housed in standard stainless steel rabbit cages, one female to a cage.
ENVIRONMENTAL CONDITIONS:
Room temperature was maintained at 23 +/- 1°C, and relative humidity at 50 +/- 5%. Lighting was on a 12 hour cycle and background music was employed to equalize ambient noises.
Administration / exposure
- Route of administration:
- other: oral/gavage in the pre-study, oral/feed and oral/gavage in the main study
- Vehicle:
- other: drinking water (gavage application, pre-study and main study), no vehicle (incorporation in food, main study)
- Details on exposure:
- PRE-STUDY:
Except for the untreated control group, the females were dosed with either the test material in water or water alone on days 2 through 16 (day inseminated = day 1). Each doe recieved 2 mL of fluid per kg bw. Dosing was commenced prior to implantation (day 7) so that any possible preimplantation effects might be revealed. The compound was given as an aqueous mixture by intubation.
MAIN STUDY:
In the main study, doses of 25, 50 or 100 mg/kg bw/day were used. The compound was incorporated into ground rabbit feed which was then repelleted and fed to the rabbits from day 2 through day 16 of pregnancy.
To determine whether the ingestion of HEDP-2Na in the feed might cause different effects than when introduced by gavage, another group of rabbits was given 100 mg/kg bw/day of the material by stomach tube just as was done in the Pre-study. Control groups, untreated and water-treated, were included. - Analytical verification of doses or concentrations:
- no
- Details on mating procedure:
- Females were artificially inseminated by the method of Gibson et al (1966).
- Duration of treatment / exposure:
- Gestation Day 2-16
- Frequency of treatment:
- Daily
- Duration of test:
- 29 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- Control group
- Dose / conc.:
- 25 mg/kg bw/day
- Dose / conc.:
- 50 mg/kg bw/day
- Dose / conc.:
- 100 mg/kg bw/day
- No. of animals per sex per dose:
- Pre-study: 25
Main study: 20 - Control animals:
- yes, concurrent no treatment
- yes, concurrent vehicle
- Details on study design:
- PRE-STUDY:
The females were artificially inseminated by the method of Gibson et al (1966) and except for the untreated controls, were dosed with either the test material in water or water alone on days 2 through 16 (day inseminated = day 1). Each doe recieved 2 mL of fluid per kg bw. Dosing was commenced prior to implantation (day 7) so that any possible preimplantation effects might be revealed. The compound was given as an aqueous mixture by intubation. Mortality was observed in animals receiving 500 mg/kg bw/day after day 4 or 5 of dosing. Consequently, the 500 mg/kg bw/day dosage was reduced to 250 mg/kg bw/day. Pregnant animals were sacrificed on day 29 and examined for resorptions, corpora lutea and implantations. The foetuses were dried of amniotic fluid, sexed, carefully inspected for gross abnormalities and weighed. One-third of the fetuses were cleared, stained with Alizarin red stain (Staples and Schnell, 1964) and examined for skeletal defects. The remaining two-thirds of the fetuses were examined for soft-tissue anomalies, either by histological methods or by freehand sectioning (Wilson, 1965).
MAIN STUDY:
Due to observed maternal toxicity from the 500 mg/kg bw/day dose of HEDP-2Na in the pre-study, doses of 25, 50 and 100 mg/kg bw/day were used. The compound was incorporated into ground rabbit feed (Purina Rabbit Chow) which was then repelleted and fed to the rabbits from day 2 through day 16 of pregnancy.
To determine whether the ingestion of HEDP-2Na in the feed might cause different effects than when introduced by gavage, another group of rabbits was given 100 mg/kg bw/day of HEDP-2Na by a stomach tube, similarly performed as in the pre-study. Control groups, untreated and water-treated animals were included.
To reduce the possibilty of a dietary bias, all rabbits were fed ground feed which had been repelleted during both the orientation period and the 29 days of gestation.The feed consumed by 25 animals was measured for 14 days during the orientation period to establish the dietary level of test substance to be incorporated into the diet. Additionally, the feed consumed from day 2 through day 16 of pregnancy was measured for all animals to determine the actual amount of HEDP-2Na ingested as well as determine whether the stress of intubing the rabbits affected feed intake.
All animals were inseminated by the method of Gibson et al., 1966 and weighed on that day and again on day 29 of pregnancy. The former weights were used to calculate the dose levels, whether given by intubation or incorporated into the feed. Those given the HEDP-2Na by stomach tube and water-treated controls were weighed daily, since this caused no additional trauma, in order to monitor the weight gains throughout gestation.
Likewise, the laparotomies and collection of data were done as described in the pre-study.
Examinations
- Maternal examinations:
- Pregnant does were examined for resorptions, corpora lutea and implantations. The body weight was recorded on GD0 and GD29. The food intake was recorded daily.
- Fetal examinations:
- The foetuses were dried of amniotic fluid, sexed, carefully inspected for gross abnormalities and weighed. One-third of the foetuses were cleared, stained with Alizarin red stain (Staples and Schnell, 1964) and examined for skeletal defects. The remaining two-thirds of the foetuses were examined for soft-tissue anomalies, either by histological methods or by freehand sectioning (Wilson, 1965).
- Statistics:
- Analyses of variance were done on the appropriate data (Snedecor, 1946), and the partitioning was done by the Tukey "minimum difference" test as described by Scheffe (1952).
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- not examined
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- Mortality was observed in the pre-study in animals receiving 500 mg/kg bw/day after day 4 or 5 of dosing. Four females that received only 3 doses of 500 mg/kg bw/day before having the dose reduced to 250 mg/kg bw/day survived to term. They were not included in the statistical analyses, however, their data were included so limited comparisons between the two doses could be performed.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- There were no statistically significant differences in the gain in bodyweight among the rabbits. The group intubated with 100 mg/kg bw/day of HEDP-2Na consumed the least amount and gained the least amount of weight during gestation.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- There were no statistically significant differences in the feed consumption among the rabbits.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Endocrine findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not examined
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- In the pre-study, renal tubular degeneration was observed in all dams administered 250 and 500 mg/kg bw/day as well as in 20% of those dosed with 100 mg/kg bw/day. However, control animals were similarly affected (occurrence of 50%) and therefore, it was not considered as treatment-related effects.
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
Maternal developmental toxicity
- Number of abortions:
- effects observed, non-treatment-related
- Description (incidence and severity):
- One dam administered 100 mg/kg bw/day of HEDP-2Na by a stomach tube, aborted at 23 days and the foetuses were dead. However, this was attributed to severe respiratory disease and is considered not as a treatment-related effect.
- Pre- and post-implantation loss:
- no effects observed
- Description (incidence and severity):
- There were no significant differences in implantations.
- Total litter losses by resorption:
- no effects observed
- Description (incidence and severity):
- There were no significant differences in resorptions.
- Early or late resorptions:
- no effects observed
- Description (incidence and severity):
- There were no significant differences in resorptions.
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- not examined
- Changes in number of pregnant:
- effects observed, non-treatment-related
- Description (incidence and severity):
- In the pre-study, New Zealand rabbits were successfully inseminated in 81% of the attempts, although this varied significantly from 100% in the water-dosed control to 68% in the group treated with 100 mg/kg bw/day of HEDP-2Na. In the main study, the overall conception rate for the 120 rabbits was 92.5% and varied from 85% in the non-treated control group to 100% in the water-treated controls. The conception rates for the HEDP-2Na-treated groups were 90% or 95% respectively, indicating the test material had no effect on conception or on nidation.
- Other effects:
- no effects observed
- Description (incidence and severity):
- No significant differences in the numbers of corpora lutea was observed.
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- >= 100 mg/kg bw/day
- Basis for effect level:
- other: No adverse effects observed
- Remarks on result:
- other: equivalent to 82.4 mg/kg bw/day active acid
Maternal abnormalities
- Abnormalities:
- not specified
Results (fetuses)
- Fetal body weight changes:
- not examined
- Reduction in number of live offspring:
- no effects observed
- Description (incidence and severity):
- In the pre-study, the number of live foetuses was reduced in the group administered 100 mg/kg bw/day, however, this was not significant and was not observed in the main study.
- Changes in sex ratio:
- not examined
- Changes in litter size and weights:
- effects observed, non-treatment-related
- Description (incidence and severity):
- In the pre-study, no significant differences in litter weights were observed. In the main study, foetuses from dams administered 100 mg/kg bw/day of HEDP-2Na daily by gavage, were significantly smaller than those from untreated control dams. However, they were from slightly larger litters. Their weights were not significantly different from the water-dosed control foetus weights. The difference might have been caused by the stress of intubation of the dam. Additionally, the reduced weight was within the normal variation and consequently, not considered as treatment related.
- Anogenital distance of all rodent fetuses:
- not examined
- Changes in postnatal survival:
- not examined
- External malformations:
- no effects observed
- Description (incidence and severity):
- In the pre-study, no defective foetuses (18 in total) were observed in dams intubated with higher doses of the test substance. Totally, 2 of 99 foetuses from dams intubated with 100 mg/kg bw/day were defective, however, this was considered as incidental and not as treatment-related effects. Of the 868 rabbit foetuses examined in the main study, 17 (less than 2%), were defective and the treated groups were not significantly different from the controls. Spina bifida and folded retina were the most frequent occurring defects.
- Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Totally, 30 to 40% of all foetuses in the pre-study had supernumerary ribs; most of these were bilateral. Variations in the sternebrae occurred; atrophy of the fifth sternebrae was most frequently observed. Intubation or administration of the test substance alone or in combination has affected the incidence of rib or sternal variations.
- Visceral malformations:
- not examined
- Other effects:
- not examined
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- >= 100 mg/kg bw/day
- Sex:
- male/female
- Basis for effect level:
- other: no adverse effects observed
- Remarks on result:
- other: equivalent to 82.4 mg/kg bw/day active acid
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
TABLE 1 (PRE-STUDY): EFFECTS OF INTUBATED HEDP-2Na ON REPRODUCTION AND TERATOGENY OF NEW ZEALAND RABBITS
|
Untreated control |
H2O control |
100 mg/kg |
500 mg/kg**** |
No. pregnant |
19 |
22 |
15 |
- |
Conception rate |
82.6 |
100.0 |
68.2*** |
- |
No. females dead |
1 |
1 |
2 |
20 |
Mean corpora lutea |
9.7 |
9.6 |
10.3 |
11.3 |
Mean resorptions |
1.2 |
1.1 |
1.4 |
3.3 |
Mean live fetuses |
8.0 |
7.8 |
6.7 |
9.0 |
Mean fetus weights (g) |
26.4 |
25.8 |
26.3 |
- |
No. fetuses examined |
146 |
158 |
99 |
18 |
No. with soft-tissue defects |
1 |
6 |
2 |
0 |
No. with skeletal defects |
0 |
0 |
0 |
0 |
Defective fetuses (%) * |
0.6 |
3.9 |
2.0 |
0 |
Hydronephrosis |
- |
2.0** |
- |
- |
Herniated lens and folded retina |
1.1 |
- |
- |
- |
Aortic arch stenosis |
- |
2.0 |
- |
- |
Missing right kidney and ureter |
- |
1.0 |
- |
- |
Cor biloculare |
- |
1.0 |
- |
- |
Testicular atrophy |
- |
1.0 |
- |
- |
Hydroencephaly |
- |
- |
1.5 |
- |
Spina bifida |
- |
- |
1.5 |
- |
* Based on total number of fetuses examined
** More than one defect may have appeared in 1 fetus
*** Significantly less than H2O dosed control (p<0.05)
**** The dosage was reduced to 250 mg/kg, but most died. Four survived: two were sacrificed early and two completed pregnancies. Their values were not included in statistical analyses.
TABLE 2 (MAIN STUDY): EFFECTS OF HEDP-2Na ON THE REPRODUCTION AND TERATOGENY OF NEW ZEALAND RABBITS
|
Untreated |
H2O |
25 |
50 |
100 |
100 mg/kg |
No. pregnant |
17 |
20 |
18 |
19 |
19 |
18 |
Conception rate |
85 |
100 |
90 |
95 |
95 |
90 |
Mean corpora lutea |
10.8 |
10.1 |
9.9 |
9.7 |
10.4 |
11.6 |
Mean resorptions |
0.9 |
0.9 |
0.9 |
1.8 |
1.2 |
0.9 |
Mean live fetuses |
7.8 |
8.0 |
8.5 |
7.1 |
8.4 |
9.4 |
Mean fetus weights (g) |
32.0 |
30.8 |
30.9 |
30.0 |
28.0 |
27.3* |
No. fetuses examined |
127 |
155 |
151 |
134 |
156 |
145 |
No. with soft-tissue defects |
2 |
4 |
1 |
1 |
4 |
4 |
No. with skeletal defects |
0 |
1 |
0 |
0 |
0 |
0 |
Defective fetuses (%) ** |
1.6 |
3.2 |
0.7 |
0.8 |
2.6 |
2.8 |
Spina bifida |
- |
1.9 |
0.7 |
- |
0.6 |
- |
Hydroencephaly |
- |
0.6 |
- |
- |
0.6 |
- |
Testicular atrophy |
0.8 |
- |
- |
- |
- |
0.7 |
Cryptorchism |
0.8 |
- |
- |
- |
- |
- |
Folded retina |
0.6 |
- |
- |
0.8 |
0.6 |
- |
Coloboma |
- |
0.6 |
- |
- |
- |
- |
Anopthalmia |
- |
- |
- |
- |
0.6*** |
- |
Arrhinencephalia |
- |
- |
- |
- |
0.6 |
- |
Bilateral hydronephrosis |
- |
- |
- |
- |
0.6 |
- |
Gastroschisis |
- |
- |
- |
- |
0.6 |
- |
Coarctation of aorta |
- |
- |
- |
- |
- |
0.7 |
* Significantly less than the nontreated control group only (p<0.05)
** Based upon total number examined
*** More than one defect may have been present in a fetus
Applicant's summary and conclusion
- Conclusions:
- In a developmental toxicity study (reliability score 2), conducted according to OECD Test Guideline 414 and pre-GLP, HEDP (2-3Na) was administered to in concentrations of 0, 25, 50 or 100 mg/kg bw/day to 20 New Zealand rabbits. A maternal and developmental NOAEL of ≥ 100 mg/kg bw/day is concluded for rabbits.
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