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EC number: 234-433-3 | CAS number: 12003-65-5
- 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2016-07-22 to 2016-08-29
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 1995
- Deviations:
- yes
- Remarks:
- see "Principles of method if other than guideline"
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 2008
- Deviations:
- yes
- Remarks:
- see "Principles of method if other than guideline"
- Principles of method if other than guideline:
- The test was performed according to the OECD-Guideline for Testing of Chemicals No. 105, Water Solubility, flask method with the following modifications:
- Two vessels were set up in a parallel design at 20.0 °C, each vessel was sampled several times instead of sampling just one vessel every time or setting up individual vessels that are sampled only once. This modification helps avoiding weighing errors and enables several samplings from two vessels, i.e., solubility measurements from two individual flasks at each defined time point. The avoidance of weighing errors and the repeated sampling from two separate vessel at each time point (as described above) helps generating more accurate and precise test results.
- The study was performed under inert gas (argon) and under exclusion of atmospheric oxygen and carbon dioxide.
- Constant concentrations (i.e. “[…] concentrations measured in at least the two last [… sampling points] do not differ by more than 15 %”), could not be measured over the course of the test for all metals. Dissolved aluminium concentrations decreased whereas lanthanum concentrations varied during the test. - GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 2016-05-31
- Type of method:
- flask method
- Key result
- Water solubility:
- < 0.05 mg/L
- Conc. based on:
- element (dissolved fraction)
- Remarks:
- Al and La
- Loading of aqueous phase:
- 100 mg/L
- Incubation duration:
- >= 5 - <= 34 d
- Temp.:
- 20 °C
- pH:
- >= 6.8 - <= 8.4
- Remarks on result:
- other: mean result from (i) filtration + centrifugal filtration
- Details on results:
- Temperature
The temperature in the thermostatically controlled water bath was monitored with a thermo data logger (Testo 175-T2, Testo AG, Leutkirch, Germany). The mean temperature was 19.6 ± 0.1 °C.
The pH
The pH of solutions containing the test item increased from 6.8 – 7.2 to 8.3 – 8.4 after 18 days of testing. Afterwards, the pH remained relatively stable at 8.2 – 8.3. The pH of method blanks ranged from 6.3 to 6.5, except for the pH in vessel 2 after 5 days (pH of 7.1), 6 and 7 days (pH of 7.8). However, the pH of the method blank in vessel 2 remained relatively stable at 6.4 – 6.6 after 18 days until the end of the test.
Oxygen concentration
During the test, the oxygen concentration in the acrylic glass box was monitored with a MICRO IV oxygen sensor prior and after sampling. Oxygen concentrations (in %) remained at about 0 %.
Turbidity
Since the sampling volume was limited, the turbidity was measured on each sampling date only in samples filtered through a 0.2 µm membrane (additional 10 mL). The turbidity of the respective centrifugal filtered test sample and method blank was only measured on day 5 with 0.02 NTU.
The turbidity was recorded for all 0.2 µm filtered samples. Turbidity of drinking water should not be > 5 NTU and should ideally be < 0.1 NTU for an effective disinfection. Thus, based on the turbidity measurement, the solution samples were clear. - Conclusions:
- Under the conditions of this test (OECD 105 (1995) flask method; loadings of 100.036 mg/L and 100.018 mg/L in vessel 1 and 2), a solubility equilibrium was not observed during the test period of 34 days. Slightly higher aluminium and lanthanum concentrations were measured in solutions filtered only through a 0.2 µm membrane in comparison to concentrations of solutions applied to centrifugal filtration.
Mean measured dissolved aluminium and lanthanum concentrations fluctuate from < 1.17 µg Al/L to 56.73 µg Al/L (background-corrected) and < 0.10 µg La/L to 13.38 µg La/L during the 34-d test period.
Based on means of dissolved Al and La concentrations (as measured on day 5, 6, 7, 18, 19, 20, 32, 33, 34) amounting to 24.25 ± 19.68 µg Al/L and 5.04 ± 5.06 µg La/L, the water solubility of aluminium lanthanum trioxide is estimated with < 0.05 mg/L.
Reference
Under the conditions of this test (flask method; loadings of 100.036 mg/L and 100.018 mg/L in vessel 1 and 2), a solubility equilibrium was not observed during the test period of 34 days. Slightly higher aluminium and lanthanum concentrations were measured in solutions filtered only through a 0.2 µm membrane in comparison to concentrations of solutions applied to centrifugal filtration. This may indicate that smaller particles (i.e. < 0.2 µm but > 3 kDa) are present in solutions filtered through a 0.2 µm membrane. Thus, aluminium and lanthanum concentrations measured in the fraction < 3 kDa are operationally defined as “dissolved concentrations”.
Measured aluminium and lanthanum concentrations of test solutions are compiled in following tables.
Mean aluminium concentrations of solutions containing the test item
A) Solutions after filtration through a 0.2 µm membrane and centrifugal filtration |
||||||
Sampling [d] |
Mean Al conc [µg/L] |
Mean SD Al conc. [µg/L] |
Variation between sampling intervals [%] |
Mean Al conc. - background- corrected [µg/L] |
Mean SD Al conc. [µg/L] |
Variation betweensampling intervals - background-corrected[%] |
5 |
47.52 |
17.81 |
|
46.49 |
17.81 |
|
6 |
56.73 |
26.03 |
19.4 |
55.18 |
26.03 |
18.7 |
7 |
33.82 |
14.62 |
-40.4 |
30.00 |
14.62 |
-45.6 |
18 |
11.77 |
15.33 |
-65.2 |
11.77 |
15.33 |
-60.8 |
19 |
4.95 |
5.69 |
-57.9 |
4.95 |
5.69 |
-57.9 |
20 |
<LOD (<1.32) |
|
|
0.93* |
|
|
32 |
32.70 |
15.72 |
|
32.70 |
15.72 |
|
33 |
31.06 |
10.30 |
-5.0 |
31.06 |
10.30 |
-5.0 |
34 |
at least <LOQ (<1.17) |
|
|
0.40# |
|
|
B) Solutions after filtration through a 0.2 µm membrane |
||||||
Sampling [d] |
Mean Al conc [µg/L] |
Mean SD Al conc. [µg/L] |
Variation between sampling intervals [%] |
Mean Al conc. - background- corrected [µg/L] |
Mean SD Al conc. [µg/L] |
Variation betweensampling intervals - background-corrected[%] |
5 |
248.67 |
58.55 |
|
246.96 |
58.55 |
|
6 |
236.34 |
74.39 |
-5.0 |
235.24 |
74.39 |
-4.7 |
7 |
197.18 |
89.70 |
-16.6 |
194.71 |
89.70 |
-17.2 |
18 |
174.14 |
39.18 |
-11.7 |
174.14 |
39.18 |
-10.6 |
19 |
169.34 |
45.90 |
-2.8 |
169.34 |
45.90 |
-2.8 |
20 |
60.33 |
74.00 |
-64.4 |
60.33 |
74.00 |
-64.4 |
32 |
85.58 |
36.86 |
41.8 |
85.58 |
36.86 |
41.8 |
33 |
71.75 |
23.98 |
-16.2 |
71.75 |
23.98 |
-16.2 |
34 |
<LOD (<0.39) |
|
|
0.28* |
|
|
* All concentrations below LOD;#All concentrations below LOD/LOQ
Mean lanthanum concentrations of solutions containing the test item
A) Solutions after filtration through a 0.2 µm membrane and centrifugal filtration |
|||
Sampling [d] |
Mean La conc. [µg/L] |
Mean SD La conc. [µg/L] |
Variation between sampling intervals [%] |
5 |
6.34 |
2.35 |
|
6 |
4.79 |
6.56 |
-24.5 |
7 |
12.76 |
17.46 |
166.7 |
18 |
0.07* |
|
|
19 |
0.93 |
1.12 |
|
20 |
5.10 |
5.79 |
469.6 |
32 |
1.25 |
1.07 |
-75.5 |
33 |
0.79 |
0.92 |
-36.9 |
34 |
13.38 |
4.47 |
1598.7 |
B) Solutions after filtration through a 0.2 µm membrane |
|||
Sampling [d] |
mean La conc. [µg/L] |
mean SD La conc. [µg/L] |
variation between sampling intervals [%] |
5 |
5.11 |
7.02 |
|
6 |
13.61 |
19.04 |
166.2 |
7 |
24.98 |
34.73 |
83.5 |
18 |
0.22 |
0.21 |
-99.1 |
19 |
0.07* |
|
|
20 |
9.73 |
13.36 |
|
32 |
0.20# |
|
|
33 |
0.25 |
0.07 |
|
34 |
24.20 |
26.74 |
9521.5 |
* All concentrations below LOD;#All concentrations below LOQ
Mean measured dissolved aluminium and lanthanum concentrations fluctuate from < 1.17 µg Al/L to 56.73 µg Al/L (background-corrected) and < 0.10 µg La/L to 13.38 µg La/L during the 34-d test period. Based on means of dissolved Al and La concentrations (as measured on day 5, 6, 7, 18, 19, 20, 32, 33, 34) amounting to 24.25 ± 19.68 µg Al/L and 5.04 ± 5.06 µg La/L, solubility of aluminium lanthanum oxide is estimated with < 0.05 mg/L.
Method validation summary (dilution with 0.5 M nitric acid)
validation parameter |
results |
comment |
selectivity |
Aluminium at wavelengths 167.019 nm and 394.402 nm Lanthanum at wavelength 379.477 nm |
no matrix effects observed |
linearity |
applied calibration functions were linear |
correlation coefficient ≥ 0.999633 |
limits of detection (LOD) |
Al: 0.0767 – 2.9037 µg/L La: 0.1004 – 0.2091 µg/L |
|
limits of quantification (LOQ) |
Al: 0.2301 – 8.7110 µg/L La: 0.3011 – 0.6272 µg/L |
|
method blanks |
Al: some method blanks >LOQ Measured test concentrations are reported without and with background correction La: Mostly <LOD, four method blanks <LOQ |
|
accuracy and precision |
mean recovery within measurement series for certified reference material TM-26.4: #1 measurement series: Al (167.019 nm): 91.9 ± 1.2 % (n = 3) |
certified with 74 µg Al/L |
accuracy and precision |
mean recoveries within measurement series for certified reference material TMDA-52.4: #2 measurement series: Al (394.402 nm): 95.4 ± 1.0 % (n = 5) #3 measurement series: Al (167.019 nm):106.8 ± 1.0 % (n = 5) |
certified with 61.2 µg Al/L (diluted 5 fold) |
accuracy and precision |
mean recovery within measurement series for multi element standard XXI: #1 measurement series: Al (167.019 nm): 94.5 ± 1.0 % (n = 3) |
diluted to 100 µg Al/L |
accuracy and precision |
mean recoveries within measurement series for recalibration samples: #2 measurement series: Al (394.402 nm): 102.1 ± 0.6 % (n = 5) La (379.477 nm): 101.8 ± 0.4 % (n = 5) #3 measurement series: Al (394.402 nm): 104.0 ± 0.6 % (n = 5) La (379.477 nm): 102.7 ± 0.5 % (n = 5) |
diluted to 100 µg Al and La/L |
accuracy and precision |
mean recovery within measurement series for recalibration samples: #1 measurement series: Al (167.019 nm): 98.5 ± 1.2 % (n = 3) La (379.477 nm): 101.1 ± 0.2 % (n = 3) |
diluted to 50 µg Al and La/L |
accuracy and precision |
mean recovery within measurement series for recalibration samples: #1 measurement series: La (379.477 nm): 110.5 ± 0.1 % (n = 3) |
diluted to 25 µg La/L |
accuracy and precision |
mean recovery within measurement series for recalibration samples: Non GLP preliminary test: Al (167.019 nm): 103.7 % (n = 1) La (379.477 nm): 106.7 % (n = 1) |
diluted to 10 µg Al and La/L |
accuracy and precision |
mean recovery within measurement series for quality control single element standard La from CPI: #1 measurement series: La (379.477 nm): 109.1 ± 0.4 % (n = 3) |
diluted to 25 µg La/L |
accuracy and precision |
mean recovery within measurement series for quality control single element standard La from CPI: #2 measurement series: La (379.477 nm): 100.3 ± 0.4 % (n = 5) #2 measurement series: La (379.477 nm): 106.6 ± 1.1 % (n = 5) |
diluted to 50 µg La/L |
trueness |
recovery from fortification of samples: Al: 92.8 – 121.0 % (n = 8) La: 100.7 – 111.0 % (n = 8) |
The recovery of Al in one sample (121.0 %) is not within the limits of 100 ± 15 %. Since recovery of 7 out of 8 fortified solutions is well within the limits, the analysis of Al concentrations is considered to be valid |
Description of key information
The waters solubility of aluminium lanthanum trioxide is estimated to be < 0.05 mg/L.
Key value for chemical safety assessment
Additional information
Under the conditions of this test (OECD 105 (1995) flask method; loadings of 100.036 mg/L and 100.018 mg/L in vessel 1 and 2), a solubility equilibrium was not observed during the test period of 34 days. Slightly higher aluminium and lanthanum concentrations were measured in solutions filtered only through a 0.2 µm membrane in comparison to concentrations of solutions applied to centrifugal filtration.
Mean measured dissolved aluminium and lanthanum concentrations fluctuate from < 1.17 µg Al/L to 56.73 µg Al/L (background-corrected) and < 0.10 µg La/L to 13.38 µg La/L during the 34-d test period.
Based on means of dissolved Al and La concentrations (as measured on day 5, 6, 7, 18, 19, 20, 32, 33, 34) amounting to 23.72 ± 20.12 µg Al/L and 5.04 ± 5.06 µg La/L, the waters solubility of aluminium lanthanum trioxide is estimated with < 0.05 mg/L.
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