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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Endpoint:
acute toxicity: inhalation
Type of information:
experimental study
Adequacy of study:
supporting study
Study period:
1980
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
comparable to guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1980
Report date:
1980

Materials and methods

Test guideline
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 403 (Acute Inhalation Toxicity)
GLP compliance:
no
Test type:
acute toxic class method
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
[ethane-1,2-diylbis[nitrilobis(methylene)]]tetrakisphosphonic acid
EC Number:
215-851-5
EC Name:
[ethane-1,2-diylbis[nitrilobis(methylene)]]tetrakisphosphonic acid
Cas Number:
1429-50-1
Molecular formula:
C6H20N2O12P4
IUPAC Name:
[ethane-1,2-diylbis[nitrilobis(methylene)]]tetrakisphosphonic acid
Test material form:
solid: particulate/powder

Test animals

Species:
rat
Strain:
Sprague-Dawley
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: River Breeding Laboratories, Wilmington, Massachusetts

- Animal weight: 239-263g (males), 218-240g (females)

Administration / exposure

Route of administration:
inhalation: dust
Type of inhalation exposure:
whole body
Vehicle:
air
Details on inhalation exposure:
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Wright Dust Feed cylinders using a carver hydraulic press
- Exposure chamber volume: 26.5 litre chamber
- Source and rate of air: 15 litres / minute
- System of generating particulates/aerosols: The test material was sieved through a #60 mesh sieve and packed into the Wright Dust cylinders using the Carver hydraulic press operating at 200 pounds per square inch. Dry air was passed through a modified Wright Dust Feed generator with a specially machined cutting blade to generate a dust laden atmosphere.


TEST ATMOSPHERE
- Brief description of analytical method used: The cylinders, cutting blade and nozzle were weighed before and after the exposure. The difference in weight represented the total amount of test material delievered into the test chamber; this divided by the total volume of air delivered yielded the nominal exposure concentration. Air samples were withdrawn each hour for gravimetric determination of the airborne concentration; these samples were withdrawn for determination of the particle size distribution using castella Cascade Impactor.
- Samples taken from breathing zone: yes

- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): 2.7 microns / 2-2.7

Analytical verification of test atmosphere concentrations:
yes
Duration of exposure:
4 h
Concentrations:
4.60 mg/l (3.78-5.17 mg/l) i.e. approximately 30% of the nominal value which was 15.5 mg/l
No. of animals per sex per dose:
5M, 5F
Control animals:
no
Details on study design:
- Duration of observation period following administration: 14 days

- Frequency of observations and weighing: The animals were observed for abnormal signs before exposure, every 15 minutes for first hour, hourly thereafter, upon removal from the chamber hourly for four hours post-exposure and daily thereafter for 14 days. Individual body weights for all rats were recorded on day 0 (prior to exposure) and on days 1,2,4,7 and 14.

- Necropsy of survivors performed: yes

Results and discussion

Effect levels
Key result
Sex:
male/female
Dose descriptor:
LC50
Effect level:
> 4.6 mg/L air (analytical)
Based on:
test mat.
Remarks on result:
other: dust
Mortality:
There were no mortalities.
Clinical signs:
other: Beginning ca. 15 minutes after initiation of exposure: hypoactivity, salivation, red nasal discharge, swollen eyelids, lacrimation, rapid or laboured respiration and soft stool were observed. Due to the density of the dust cloud visibility of the animals
Body weight:
Transient body weight losses were seen in most rats but in most cases these had recovered to the starting weights by day 4 or 7. Weight gains in the second week were within the range of normal expectation.
Gross pathology:
At necropsy lung discolouration was seen in all males and two females. These are common macropathological entities in this strain of rat but the incidence in males may reflect a slight response to treatment, especially if viewed in conjunction with the in vivo evidence of irritant effects on the ocular, buccal, nasal and respiratory mucosae on the day of exposure.
Other findings:
None reported.

Applicant's summary and conclusion

Interpretation of results:
GHS criteria not met
Conclusions:
An LC50 value of 4.60 mg/l (3.78-5.17 mg/l) i.e. approximately 30% of the nominal value which was 15.5 mg/l is reported in a reliable study conducted according to a protocol equivalent to current guideline. The study was not compliant with GLP.