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EC number: 231-633-2 | CAS number: 7664-38-2
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- 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
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
See read-across justification report under Section 13 ‘Assessment Reports’.
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
In accordance with REACH Annex XI, Section 1.5, of Regulation (EC) No. 1907/2006 (REACH) the standard testing regime may be adapted in cases where a grouping or read-across approach has been applied.
The similarities may be based on:
(1) a common functional group
(2) the common precursors and/or the likelihood of common breakdown products via physical or biological processes, which result in structurally similar chemicals; or
(3) a constant pattern in the changing of the potency of the properties across the category
The source chemical and orthophosphoric acid have the following similarities:
(1) All substances are ionic and share the PO43-anion as a common functional groups.
(2) All members of the group will ultimately dissociate into the common breakdown products of the Na+or K+cations (for sodium and potassium orthophosphates respectively) and the PO43-anion (all). Thus phosphoric acid is systemically bioavailable as phosphate.
3) Sodium aluminium phosphate is essentially a sodium orthophosphate that also contains an aluminium ion. Although aluminium is known to have toxic effects, no evidence of aluminium toxicity was observed in any of the studies. The addition of aluminium in the phosphate compound is unlikely to have an impact on the use of this data for the sodium and potassium phosphates as any toxicity observed is considered to be due to the phosphate content of the test material; renal effects (nephrocalcinosis) indicative of high phosphate intake were the only toxic effects noted in the studies. Therefore the results of the tests performed with sodium aluminium phosphate can reliably be read across to orthophosphoric acid. This conclusion is further supported by the data on a number of analogous substances which suggests potassium and sodium orthophosphates and orthophosphoric acid itself are not considered to be systemically toxic.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
See read-across justification report under Section 13 ‘Assessment Reports’.
3. ANALOGUE APPROACH JUSTIFICATION
See read-across justification report under Section 13 ‘Assessment Reports’.
4. DATA MATRIX
See read-across justification report under Section 13 ‘Assessment Reports’.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 972
- Report date:
- 1972
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- A 90-day oral toxicity study was conducted with groups of albino rats fed Levn-Lite at dietary levels of 0.3, 1.0 and 3.0%.
- GLP compliance:
- no
- Remarks:
- Study predates GLP
- Limit test:
- no
Test material
- Reference substance name:
- Phosphoric acid, aluminium sodium salt
- EC Number:
- 232-090-4
- EC Name:
- Phosphoric acid, aluminium sodium salt
- Cas Number:
- 7785-88-8
- Reference substance name:
- sodium aluminium phosphate (3:2:8)
- IUPAC Name:
- sodium aluminium phosphate (3:2:8)
- Test material form:
- other: solid
- Details on test material:
- - Name of test material (as cited in study report): Levn-Lite
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- not specified
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Inc., North Wilmington, Mass.
- Age at study initiation: No data
- Weight at study initiation: Males: 185-187 g; Females: 149-150 g
- Housing: Animals were housed individually in standard, wire-bottomed steel rat cages.
- Diet: standard rat ration available ad libitum
- Water: No data
- Acclimation period: No data
ENVIRONMENTAL CONDITIONS
No data
IN-LIFE DATES: No data
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: No data
DIET PREPARATION
- Rate of preparation of diet: Fresh diets were prepared each week. Each rat was offered an amount of diet sufficient for one weeks' ad libitum feeding. However, checks were made periodically to ensure that the food jars were not empty.
- Diet prepared by mixing appropriate amounts with standard rat ration in a Hobart Mixer.
VEHICLE
Not applicable - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- Not applicable
- Duration of treatment / exposure:
- 90 day exposure
- Frequency of treatment:
- Continuous exposure in feed
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0.3, 1.0 and 3.0%
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
Male: 155.36, 545.64 and 1796.95 mg/kg bw/day Female: 181.18, 701.65 and 2070.10 mg/kg bw/day
Basis:
other: Calculated using the mean of the weekly body weight and food consumption
- No. of animals per sex per dose:
- 15 animals/sex/dose
- Control animals:
- yes, plain diet
- Details on study design:
- No data
- Positive control:
- Not applicable
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Daily
BODY WEIGHT: Yes
- Time schedule for examinations: Each animal was weighed on the first day of the test and at weekly intervals thereafter.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
Food consumption data were collected individually for 5 rats of each sex in every group weekly during the study.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: after 45 and 84 days of feeding
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: collected individually from 10 rats of each sex from both the control and the high dose group
- Parameters: haematocrit value, erythrocyte count, haemolglobin concentration, total leukocyte count, differential leukocyte count
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: after 45 and 84 days of feeding
- Animals fasted: No data
- How many animals: collected individually from 10 rats of each sex from both the control and the high dose group
- Parameters: blood urea nitrogen (BUN) concentration, serum alkaline phosphatase (SAP) activity, serum glutamic-pyruvic transaminase (SGPT) activity, fasted blood glucose concentration
URINALYSIS: Yes - collected individually from 10 rats of each sex from both the control and the high dose group
- Time schedule for collection of urine: after 45 and 84 days of feeding
- Metabolism cages used for collection of urine: No data
- Animals fasted: No data
- Parameters: glucose concentration, albumin concentration, microscopic elements examination, pH, specific gravity
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- Following 90 days of feeding, all surviving rats were sacrificed by carbon dioxide asphyxiation and autopsied. At the time of gross examination a complete set of organs and other tissues were removed from each rat and preserved in formalin solution.
GROSS PATHOLOGY: Yes
Organ weights were determined for the liver, kidneys, spleen, gonads, heart and brain of each rat.
HISTOPATHOLOGY: Yes
Microscopic examination of tissues was performed for 10 rats of each sex from both the control and the high dose group. The following tissues were included: oesophagus, stomach (cardia, funuds and pylorus), small intestine (duodenum, jejunum and ileum), caecum, colon, liver, kidneys, spleen, pancreas, urinary bladder, pituitary gland, adrenal gland, testes, seminal vesicle, ovary, bone marrow, thyroid gland, parathyroid gland, salivary gland, prostate gland, heart, aorta, lung, lymph node (cervical and mesenteric), skeletal muscle, peripheral nerve, bone (femur), spinal cord, uterus, trachea, eye, optic nerve and brain (cerebrum, cerebellum and pons) - Other examinations:
- None
- Statistics:
- Statistical analyses were conducted upon the absolute organ weights and their corresponding ratios to the weight of the body and brain. An analysis of variance was conducted first and any significant effects disclosed by that treatment were further studies by "t" tests.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- CLINICAL SIGNS AND MORTALITY
Three deaths occurred during the study. All of these deaths resulted from trauma incurred during the collection of blood samples.
No untoward behavioural reactions were noted among any of the animals employed in the study.
BODY WEIGHT AND WEIGHT GAIN
Statistical comparisons of final body weights and total weight gains revealed no significant differences between test and control rats. The 90 day average total weight gains were:
Control: Male: 337 g/rat; Females: 181 g/rat
0.3%: Male: 395 g/rat; Females: 162 g/rat
1.0%: Male: 355 g/rat; Females: 157 g/rat
3.0%: Male: 355 g/rat; Females: 148 g/rat
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
Test rats ate amounts of food comparable to that consumed by control rats. The 90 day average total food consumption was:
Control: Male: 2296 g/rat; Females: 1705 g/rat
0.3%: Male: 2318 g/rat; Females: 1566 g/rat
1.0%: Male: 2127 g/rat; Females: 1570 g/rat
3.0%: Male: 2194 g/rat; Females: 1680 g/rat
HAEMATOLOGY
No outstanding differences between test and control rats were noted with respect to any of the parameters investigated (see Tables 1 and 2).
CLINICAL CHEMISTRY
Values for test rats were not different from those of control rats (see Tables 3 and 4).
URINALYSIS
No significant differences between the urine of the test rats and control rats were observed (see Table 5).
ORGAN WEIGHTS (see Table 6)
The number of statistically significant intergroup differences which were noted was considered to be normal for a random population of albino rats. The lack of any consistent dose or sex related response and the absence of any deleterious histopathological changes further substantiate that none of the intergroup differences were related to the ingestion of Levn-Lite.
No statistically significant treatment effects were found in the liver, spleen
Statistically significant differences were seen at the 95% confidence level in the kidneys at the 3.0% dose level.
Statistically significant differences were seen at the 99% confidence level in the gonads at the 0.3% dose level.
GROSS PATHOLOGY
No outstanding differences were noted between test and control rats upon gross pathological examination.
HISTOPATHOLOGY (see Table 7)
There are microconcretions present in the renal tubules of the female rats from all three dose levels. These concretions are located in the tubules at the corticomedullary junction and they consist of an amorphous material which shattered on sectioning. They are blue in colour and probably calcified. These concretions are believed to be related to the test material since they are absent in the control animals and since the incidence and severity of this finding appear to be dose related.
The other lesions observed are those of spontaneous disease and they are not unusual for the albino rat.
Effect levels
open allclose all
- Dose descriptor:
- LOAEL
- Effect level:
- 155 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Nephrocalcinosis
- Dose descriptor:
- NOAEL
- Basis for effect level:
- other: overall effects Histopathology: Microconcretions in the renal tubules of the female rats from all three dose levels
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Table 1: Haematological data – summary of mean values
Dietary level (%) |
Sex |
Total Leukocyte count (thousands/mm3) Day: |
Erythrocyte count (millions/mm3) Day |
Haemoglobinconcentration (g/100mL) Day |
Haematocritvalue (%) Day: |
||||
45 |
84 |
45 |
84 |
45 |
84 |
45 |
84 |
||
Control |
M |
17.1 |
15.9 |
7.72 |
8.08 |
15.7 |
15.9 |
39.3 |
40.5 |
- |
F |
14.7 |
9.9 |
7.70 |
7.52 |
15.5 |
15.7 |
38.4 |
37.9 |
3.0 |
M |
15.0 |
14.2 |
7.75 |
8.23 |
15.9 |
16.2 |
39.4 |
41.0 |
- |
F |
14.6 |
9.2 |
7.78 |
7.77 |
15.9 |
15.7 |
39.1 |
39.3 |
Table 2: Haematological data – summary of mean values
Dietary level (%) |
Sex |
Differential leukocyte count (No. of cells per 100) |
|||||||||
Lymphocytes Day: |
Neutrophils Day |
Monocytes Day |
Eosinophils Day |
Basophils Day |
|||||||
45 |
84 |
45 |
84 |
45 |
84 |
45 |
84 |
45 |
84 |
||
Control |
M |
90.6 |
86.7 |
8.6 |
11.1 |
0.8 |
1.7 |
0.0 |
0.5 |
0.0 |
0.0 |
- |
F |
83.2 |
85.5 |
15.2 |
12.6 |
0.8 |
1.0 |
0.8 |
0.9 |
0.0 |
0.0 |
3.0 |
M |
84.4 |
83.1 |
13.2 |
13.8 |
1.6 |
2.1 |
0.8 |
1.0 |
0.0 |
0.0 |
- |
F |
85.6 |
87.1 |
12.2 |
11.7 |
1.0 |
1.0 |
1.2 |
0.2 |
0.0 |
0.0 |
Table 3: Clinical blood chemistry data – summary of mean values
Dietary level (%) |
Sex |
Serum alkaline phosphatase activity (King-Armstrong units) Day |
Serum glutamic-pyruvic transaminase activity (Dade units) Day |
||
45 |
84 |
45 |
84 |
||
Control |
M |
31 |
24 |
30 |
27 |
- |
F |
20 |
12 |
24 |
28 |
3.0 |
M |
33 |
23 |
26 |
32 |
- |
F |
18 |
12 |
26 |
21 |
Table 4: Clinical blood chemistry data – summary of mean values
Dietary level (%) |
Sex |
Blood urea nitrogen concentration (mg %) Day |
Fasted blood glucose concentration (mg %) Day |
||
45 |
84 |
45 |
84 |
||
Control |
M |
16 |
15 |
129 |
141 |
- |
F |
17 |
14 |
130 |
137 |
3.0 |
M |
16 |
14 |
144 |
153 |
- |
F |
16 |
14 |
154 |
143 |
Table 5: Urine analysis data - summary of mean values
Dietary level (%) |
Sex |
Glucose Day |
Albumin Day |
Microscopic elements Day |
pH Day |
Specific gravity Day |
|||||
45 |
84 |
45 |
84 |
45 |
84 |
45 |
84 |
45 |
84 |
||
Control |
M |
N |
N |
T |
N |
+1 |
+2 |
7.0 |
6.8 |
1.025 |
1.039 |
- |
F |
N |
N |
N |
N |
+2 |
+1 |
7.8 |
6.8 |
1.027 |
1.036 |
3.0 |
M |
N |
N |
N |
T |
+1 |
t |
6.8 |
6.8 |
1.021 |
1.053 |
- |
F |
N |
N |
N |
T |
+1 |
+1 |
6.6 |
6.6 |
1.025 |
1.032 |
Glucose and albumin:
N = negative
T = trace; less than 30 mg/100mLurine
Microscopic elements:
t = minimal
+1 = slight amounts
+2 = moderate amounts
Table 6: Organ weight and ratio data – summary of mean results
Dietary level (%) |
Organ weight (g) |
Organ/ Body weight ratio (g/100g) |
Organ/ brain weight ratio (g/g) |
|||
Males |
Females |
Males |
Females |
Males |
Females |
|
Liver |
||||||
None |
18.140 |
10.064 |
3.4790 |
3.2526 |
8.8872 |
5.0896 |
0.3 |
19.513 |
10.862 |
3.3432 |
3.3496 |
9.4149 |
5.7542 |
1.0 |
19.024 |
9.034 |
3.4991 |
2.9358 |
9.2539 |
4.8977 |
3.0 |
17.015 |
10.119 |
3.1883 |
3.3999 |
8.1248 |
5.2737 |
Kidneys |
||||||
None |
3.666 |
2.117 |
0.7019 |
0.6798 |
1.8015 |
1.0695 |
0.3 |
3.713 |
2.134 |
0.6364 |
0.6686 |
1.7939 |
1.1141 |
1.0 |
3.739 |
2.067 |
0.6930 |
0.6688 |
1.8148 |
1.1259 |
3.0 |
3.644 |
2.227 |
0.6812 |
0.7468* |
1.7462 |
1.1639 |
Spleen |
||||||
None |
0.936 |
0.618 |
0.1805 |
0.2031 |
0.4599 |
0.3087 |
0.3 |
0.973 |
0.599 |
0.1681 |
0.1869 |
0.4684 |
0.3119 |
1.0 |
0.884 |
0.482 |
0.1641 |
0.1588 |
0.4315 |
0.2609 |
3.0 |
0.926 |
0.578 |
0.1737 |
0.1934 |
0.4445 |
0.3025 |
Gonads |
||||||
None |
3.611 |
0.077 |
0.6924 |
0.0253 |
1.7724 |
0.0392 |
0.3 |
3.537 |
0.066 |
0.6064** |
0.0208 |
1.7317 |
0.0348 |
1.0 |
3.566 |
0.083 |
0.6653 |
0.0271 |
1.7115 |
0.0449 |
3.0 |
3.638 |
0.085 |
0.6823 |
0.0285 |
1.7724 |
0.0449 |
Heart |
||||||
None |
1.613 |
1.078 |
0.3095 |
0.3484 |
0.7937 |
0.5447 |
0.3 |
1.696 |
1.093 |
0.2904 |
0.3417 |
0.8199 |
0.5724 |
1.0 |
1.674 |
1.025 |
0.3096 |
0.3365 |
0.8163 |
0.5574 |
3.0 |
1.608 |
1.001 |
0.3015 |
0.3367 |
0.7707 |
0.5230 |
Brain |
||||||
None |
2.041 |
1.982 |
0.3914 |
0.6431 |
1.0000 |
1.0000 |
0.3 |
2.076 |
1.917 |
0.3575* |
0.6038 |
1.0000 |
1.0000 |
1.0 |
2.063 |
1.838* |
0.3841 |
0.6098 |
1.0000 |
1.0000 |
3.0 |
2.086 |
1.919 |
0.3914 |
0.6457 |
1.0000 |
1.0000 |
* Statistically significant difference at the 95% confidence level
** Statistically significant difference at the 99% confidence level
Table 7:Histopathological changes
Number of animals |
Organ examined |
Findings |
Incidence |
Average grade |
Control |
||||
10 males |
Trachea |
Chronic tracheitis |
6 |
1.0 |
- |
Lung |
Chronic murine pneumonia |
3 |
1.0 |
- |
Colon |
Parasites |
1 |
1.0 |
- |
Kidney |
Focal lymphoid infiltration |
3 |
1.0 |
- |
Urinary bladder |
Mucoid plug |
6 |
1.0 |
10 females |
Lung |
Chronicmurine pneumonia |
1 |
1.0 |
- |
Colon |
Parasites |
1 |
1.0 |
Dose level: 0.3% |
||||
15 females |
Kidney |
Microconcentrations |
4 |
0.5 |
- |
- |
Hydronephrosis |
1 |
2.0 |
- |
- |
Focal lymphoid infiltration |
1 |
2.0 |
Dose level: 1.0% |
||||
10 males |
Kidney |
No findings |
- |
- |
10 females |
Kidney |
Microconcretions |
5 |
2.0 |
- |
- |
Focal lymphoid infiltration |
5 |
2.0 |
Dose level: 3.0% |
||||
10 males |
Trachea |
Chronic tracheitis |
4 |
1.0 |
- |
Lung |
Chronic murine pneumonia |
5 |
1.0 |
- |
Kidney |
Focal lymphoid infiltration |
1 |
1.0 |
- |
Urinary bladder |
Mucoid plug |
1 |
1.0 |
10 females |
Trachea |
Chronic tracheitis |
4 |
1.0 |
- |
Colon |
Parasites |
1 |
1.0 |
- |
Kidney |
Microconcentrations |
9 |
1.0 |
|
|
Focal lymphoid infiltration |
1 |
1.0 |
All other tissues and organs were normalhistologically.
Grading system:
0.5 = minimal
1.0 = slight
2.0 = mild
3.0 = moderate
4.0 = severe
5.0 = extreme
Applicant's summary and conclusion
- Conclusions:
- Results obtained from microscopic examination of tissues and organs disclosed microconcretions (nephrocalcinosis) in the renal tubules of the female rats from all three test groups. These concretions are believed to be related to the test material since they are absent in the control animals and since the incidence and severity of this finding appear to be dose related. No abnormalities were observed in body weight gains, food consumption, haematologic studies, clinical blood chemistry studies, urine analyses, gross pathological studies and organ weights and ratios. As no NOAEL was determined, this study is not preferred for use as a key study to derive the DNELS for use in risk assessment however it is considered to be a worst-case option for the derivation on an oral DNEL for the general population.
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