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EC number: 231-823-5 | CAS number: 7757-86-0
- 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
Oral (OECD 420, RL1), rat LD50 > 2000 mg/kg bw (limit test)
There is no reliable data availabe regarding acute dermal toxicity for magnesium hydrogenorthophosphate. Read across data with calcium bis (dihydrogenorthophosphate) CAS 7758 -23 -8 is used and considered reliable.
Dermal (similar to OECD 402, CAS 7758 -23 -8, RL2), rabbit, LD50 > 2000 mg/kg bw (limit test)
There is no data regarding acute toxicity via inhalation route available for magnesium hydrogenorthophosphate. Read across data with calcium bis (dihydrogenorthophosphate) CAS 7758 -23 -8 is used and considered reliable.
Inhalation (OECD 403, CAS 7758 -23 -8, RL1), rat LC50 > 2.6 mg/L air (limit test)
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- The study was performed between 11 March 2010 and 06 April 2010.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 420 (Acute Oral Toxicity - Fixed Dose Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 bis (Acute Oral Toxicity - Fixed Dose Procedure)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- fixed dose procedure
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Remarks:
- HsdRccHan®™:WIST®™
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories UK Limited, Bicester, Oxon, UK
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: eight to twelve weeks
- Weight at study initiation: mean 177 g
- Fasting period before study: overnight
- Housing: n groups of up to four in suspended solid floor polypropylene cages furnished with woodflakes
- Diet: ad libitium - 2014 Teklad Global Rodent diet supplied by Harlan Teklad, Blackthorn, Bicester, Oxon, UK
- Water: ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 25°C
- Humidity (%): 30 to 70%
- Air changes (per hr): at least 15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: To: - Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- Using available information on the toxicity of the test material, 2009 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight) was chosen as
the starting dose.
Dose Level(mg/kg) Concentration(mg/ml) Dose Volume(ml/kg) Number of Rats
Female
2009* 200.9 10 1
In the absence of toxicity at a dose level of 2009 mg/kg, an additional group of animals was treated as follows:
Dose Level(mg/kg) Concentration(mg/ml) Dose Volume(ml/kg) Number of Rats
Female
2009* 200.9 10 4
A total of five animals were therefore treated at a dose level of 2009 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight) in the study.
All animals were dosed once only by gavage using a metal cannula attached to a graduated syringe. The volume administered to each animal was
calculated according to its fasted bodyweight at the time of dosing. - Doses:
- 2009 mg/kg (equivalent to 2000 mg active ingredient /kg bodyweight)
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Clinical observations were made ½, 1, 2, and 4 hours after dosing and then daily for fourteen days. Morbidity and mortality checks were made twice daily. Individual bodyweights were recorded on Day 0 (the day of dosing) and on Days 7 and 14.
- Necropsy of survivors performed: Yes
- Other examinations performed: clinical signs, body weigh - Preliminary study:
- A sighting test at a dose level of 2009 mg/kg (equivalent to 2000 mg active ingredient /kg bodyweight) was performed.
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- act. ingr.
- Mortality:
- There were no deaths.
- Clinical signs:
- other: No signs of systemic toxicity were noted.
- Gross pathology:
- No abnormalities were noted at necropsy.
Individual necropsy findings are given in Table 3. - Interpretation of results:
- GHS criteria not met
- Conclusions:
- The acute oral median lethal dose (LD50) of the test material in the female Wistar strain rat was estimated to be greater than 2000 mg/kg bodyweight (Not classified - EU CLP).
Magnesium hydrogenorthophosphate is not considered to be classified according to Regulation (EC) No. 1272/2008 (EU CLP). Study is considered to be acceptable and to adequately satisfy both the guideline requirement and the regulatory requirement for this endpoint. Study is sufficient for classification and labelling purposes, in accordance with Regulation (EC) No. 1272/2008 (EU CLP). - Executive summary:
Introduction.
The study was performed to assess the acute oral toxicity of the test material in the Wistar strain rat. The method was designed to meet the requirements of the following:
OECD Guidelines for Testing of Chemicals No.420 "Acute Oral Toxicity - Fixed Dose Method" (Adopted 17th December 2001)
Method B1 bis Acute Toxicity (Oral) of Commission Regulation (EC) No. 440/2008
Method.
Following a sighting test at a dose level of 2009 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight), an additional four fasted female animals were given a single oral dose of test material, as asuspensionindistilled water, at a dose level of 2009 mg/kg bodyweight (equivalent to 2000 mg active ingredient/kg bodyweight). Clinical signs and bodyweight development were monitored during the study. All animals were subjected to gross necropsy.
Mortality.
There were no deaths.
Clinical Observations.
There were no signs of systemic toxicity.
Bodyweight.
All animals showed expected gains in bodyweight.
Necropsy.
No abnormalities were noted at necropsy.
Conclusion. The acute oral median lethal dose (LD50) of the test material in the female Wistar strain rat was estimated to be greater than 2009 mg/kg bodyweight (equivalent to 2000 mg active ingredient/kg bodyweight) (Not classified - EU CLP)
Reference
Table1 Individual Clinical Observations and Mortality Data
Dose Level mg/kg |
Animal Number and Sex |
Effects Noted After Dosing |
Effects Noted During Period After Dosing |
||||||||||||||||
½ |
1 |
2 |
4 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
||
2009* |
1-0 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2-0 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-1 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-2 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-3 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
*= Equivalent to 2000 mg active ingredient/kg bodyweight
0= No signs of systemic toxicity
Table2 Individual Bodyweights and Bodyweight Changes
Dose Level mg/kg |
Animal Number and Sex |
Bodyweight (g) at Day |
Bodyweight Gain (g) During Week |
|||
0 |
7 |
14 |
1 |
2 |
||
2009* |
1-0 Female |
169 |
176 |
188 |
7 |
12 |
2-0 Female |
165 |
178 |
189 |
13 |
11 |
|
2-1 Female |
169 |
182 |
190 |
13 |
8 |
|
2-2 Female |
187 |
198 |
207 |
11 |
9 |
|
2-3 Female |
195 |
210 |
216 |
15 |
6 |
*= Equivalent to 2000 mg active ingredient/kg bodyweight
Table3 Individual Necropsy Findings
Dose Level |
Animal Number |
Time of Death |
Macroscopic Observations |
2009* |
1-0 Female |
Killed Day 14 |
No abnormalities detected |
2-0 Female |
Killed Day 14 |
No abnormalities detected |
|
2-1 Female |
Killed Day 14 |
No abnormalities detected |
|
2-2 Female |
Killed Day 14 |
No abnormalities detected |
|
2-3 Female |
Killed Day 14 |
No abnormalities detected |
*= Equivalent to 2000 mg active ingredient/kg bodyweight
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
- Quality of whole database:
- The study is conducted under the conditions of GLP and in accordance with an appropriate guideline (OECD 420).
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- see analogue justification attached to chapter 13
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 2.6 mg/L air
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Mortality:
- All animals survived the scheduled observation period.
- Clinical signs:
- other: Slight to moderate ruffled fur was noted in all animals on test day 1, one hour after the end of the exposure and persisted slightly until test day 2 in nine animals. From test day 3 onwards, all animals were free from clinical signs until their scheduled
- Body weight:
- From test day 1 to test day 2, marginal to slight body weight loss was noted in all animals. Thereafter all animals gained weight until scheduled necropsy.
- Gross pathology:
- There were no macroscopic findings.
- Other findings:
- Not applicable.
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The LC50 of magnesium hydrogenorthophosphate as obtained in this study was estimated to be greater than 2.6 mg/L air (gravimetrically determined mean aerosol concentration). This was the highest technically achievable test concentration. There was no indication of relevant sex-related differences in toxicity of the test item.
In accordance with Regulation (EC) No. 1272/2008 (EU CLP) magnesium hydrogenorthophosphate is not considered to be classified as acutely toxic via the inhalation route. - Executive summary:
The LC50 was estimated to be greater than 2.6 mg/L air for magnesium hydrogenorthophosphate as found in the source study performed with calcium bis(dihydrogenorthophosphate). As explained in the justification for type of information, the differences in molecular structure between magnesium hydrogenorthophosphate and calcium bis(dihydrogenorthophosphate) are unlikely to lead to differences in the LC50 for inhalation.
Reference
The nominal aerosol concentration was 7.5 mg/L air.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 2 600 mg/m³ air
- Quality of whole database:
- The available information comprises an adequate and reliable study from a reference substance similar in structure and intrinsic properties. Read-across is justified based on structural similarities of calcium- and magnesiumphosphate compounds and their similarities in PC/ECO/TOX properties (refer to read across justification for further details). The selected study is thus sufficient to fulfill the standard information requirements set out in Annex VII, 8.5, in accordance with Annex XI, 1.5, of Regulation (EC) No. 1907/2006.
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- refer to analogue justification provided in IUCLID section 13
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- A single dermal dose of 2000 mg/kg bw produced no mortalities in a mixed group of albino rabbits (5 male and 5 female).
- Clinical signs:
- other: All rabbits in the test group and the sham-exposed control group appeared normal throughout the 14-day test.
- Gross pathology:
- 10 rabbits from the test material exposed group and 4 rabbits from the sham-exposed group were necropsied on day 14 and appeared normal.
- Other findings:
- - Other observations: local effects: Local dermal effects in the test material group included darkened dose sites, severe erythema, mild edema and the skin at the abrasion marks was separated and filled with reddish fluid and pus-like material. There were no apparent local dermal effects following a 24 hour sham-treatment.
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The dermal LD50 of magnesium hydrogenorthophosphate obtained from this study was estimated to be greater than 2000 mg/kg bw. This was the highest dose tested. There was no indication of toxic signs up to this dose.
- Executive summary:
The dermal LD50 > 2000 mg/kg bw was estimated from the dermal LD50 of the source substance calcium bis(dihydrogenorthophosphate). As explained in the justification for type of information, the differences in molecular structure between magnesium hydrogenorthophosphate and calcium bis(dihydrogenorthophosphate) are unlikely to lead to differences in the LD50.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
- Quality of whole database:
- The available information comprises an adequate and reliable study from a reference substance similar in structure and intrinsic properties. Read-across is justified based on structural similarities of calcium- and magnesiumphosphate compounds and their similarities in PC/ECO/TOX properties (refer to read across justification for further details). The selected study is thus sufficient to fulfill the standard information requirements set out in Annex VII, 8.5, in accordance with Annex XI, 1.5, of Regulation (EC) No. 1907/2006.
Additional information
Oral:
A GLP acute oral toxicity study with magnesium hydrogenorthophosphate 3 -hydrate according to OECD 420 was performed (Harlan, 2010). Following a sighting test at a dose level of 2009 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight), an additional four fasted female animals were given a single oral dose of test material, as a suspension in distilled water, at a dose level of 2009 mg/kg bodyweight (equivalent to 2000 mg active ingredient/kg bodyweight). Clinical signs and bodyweight development were monitored during the study. All animals were subjected to gross necropsy. There were no deaths, no signs of systemic toxicity and no abnormalities noted at necropsy. All animals showed expected gains in bodyweight. In conclusion, the acute oral median lethal dose (LD50) of the test material in the female Wistar strain rat was estimated to be greater than 2009 mg/kg bodyweight (equivalent to 2000 mg active ingredient/kg bodyweight).
Inhalation:
No study is available with magnesium hydrogenorthophosphate (CAS 7757 -86 -0). Reliable data is available for calcium bis(dihydrogenorthophosphate) (CAS 7758 -23 -8).
Calcium bis(dihydrogenorthophosphate) and trimagnesium bis(orthophosphate) are structurally similar ionic compounds with the only differences being that calcium is replaced with magnesium. The phosphate groups are structurally identical between the two compounds and any acute toxicity potential will be the same. Magnesium and calcium are both alkali metals from group 2 and periods 3 and 4 of the periodic table, respectively and have only one oxidation state (+2). Magnesium and calcium are among the most abundant elements and are the important essential nutrients for higher plants, algae, animals and human. Both elements are similar in chemical nature and show the related metabolism and similar environmental behaviour. The differences between the two compounds will not have an impact on any acute toxicity potential and therefore, the result from the acute inhalation toxicity study can reliably be read across to trimagnesium bis(orthophosphate).
In an inhalation toxicity study (according to OECD 403, Harlan, 2010), groups of 11 week old Wistar rats (5/sex) were exposed by inhalation route (nose only) to the test substance as a dust and observed for 14 days. The maximal achievable dose was 2.6 mg/L. The rats were exposed for 4 hours. The ranges of aerosol concentration, temperature, relative humidity, oxygen content and airflow rate measured during the exposure were considered to be satisfactory for a study of this type. In addition, the test item was considered to be respirable to rats. All animals survived the scheduled observation period. Slight to moderate ruffled fur was noted in all animals after the end of the exposure and was still present in most animals up to test day 2. Thereafter, all animals were free from clinical signs. Transient body weight loss was noted in all animals from test day 1 to test day 2. Normal body weight development was observed thereafter. No macroscopical findings were present at necropsy.
In conclusion, the LC50 of calcium bis(dihydrogenorthophosphate) and thus of magnesium hydrogenorthophosphate obtained in this study was estimated to be greater than 2.6 mg/L air (gravimetrically determined mean aerosol concentration). There was no indication of relevant sex-related differences in toxicity of the test item.
Dermal:
No reliable study is available with magnesium hydrogenorthophosphate (CAS 7757 -86 -0). Reliable data is available for calcium bis(dihydrogenorthophosphate) (CAS 7758 -23 -8).
In an acute dermal toxicity study (similar to OECD 402) with calcium bis(dihydrogenorthophosphate), groups of fasted young Stauffland albino rabbits (5/sex) were dermally exposed to the undiluted test substance for 72 hours at 2000 mg/kg bw. and observed for 14 days. The skin was abraded before treatment and test substance was hold in place by an occlusive dressing. This procedure represents a worst case scenario since the exposure duration was 72 hours instead of 24 hours and occlusive dressing and abrasion of the skin was performed. No mortality or unusual clinical signs occurred during this study. At autopsy, no abnormalities were observed. Local dermal effects in the test material group included darkened dose sites, severe erythema, mild edema and the skin at the abrasion marks was separated and filled with reddish fluid and pus-like material. In conclusion, under the conditions of this study, the LD50 of calcium bis(dihydrogenorthophosphate) and thus of magnesium hydrogenorthophosphate was considered to be >2000 mg/kg bw.
In conclusion, since calcium bis(dihydrogenorthophosphate) is a reliable read across substance and no acute inhalation or dermal toxicity are observed, magnesium hydrogenorthophsphate is considered to be also not acute toxic via dermal and inhalation route.
Justification for classification or non-classification
In accordance with Regulation (EC) No.1272/2008 (EU CLP) trimagnesium bis(orthophosphate) is not considered to be classified for acute toxicity via any route. The data provided for this endpoint are considered to be conclusive and no further investigation is required.
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