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EC number: 242-768-1 | CAS number: 19035-79-1
- 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
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Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2013-01-14 to 2013-02-27
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- The study was regarded as reliable without restrictions because it was conducted in compliance with GLP regulation and guideline.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.1 (Acute Toxicity for Fish)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- Duplicate samples from the freshly prepared test medium of the only test concentration and the control were taken at the start of the test.
For the determination of the stability of the test item under the test conditions and of the maintenance of the test item concentration during the test period, duplicate samples from the test medium of the only test concentration and the control were collected at the end of the test (after 96 hours) from the approximate centre of the aquaria. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method:
The test item was not well soluble in test water. Therefore, a stock suspension of 100 mg test item/L was prepared by suspending 1.0002 g of test item in 10.0002 L test water for preparing the test concentration. The stock suspension was stirred for 24 hours to dissolve as much test item as possible. Then, the undissolved test item was separated by filtration (0.45 µm cellulose acetate nitrate filter). The test media were prepared just before introduction of the test fish (= start of the test). - Test organisms (species):
- Oncorhynchus mykiss (previous name: Salmo gairdneri)
- Details on test organisms:
- TEST ORGANISM
- Common name: Rainbow trout
- Source: The test fish were obtained from Forellenzuchtbetrieb Störk, 88348 Bad Saulgau, Germany
- Age at study initiation: Juveniles
- Length at study initiation: 4.83 cm ± 0.30 cm
- Weight at study initiation: 1.12 ± 0.23 g
- Feeding during test: no
ACCLIMATION
- Acclimation period: All fish were obtained and held in the laboratory for at least 12 days before the start of the test.
- Acclimation conditions: same as test conditions
- Feeding frequency: three times per week or daily until 24 hours before the test was started
- Health during acclimation: During the last 7 days prior to the start of the test no fish died in the test fish batch. Therefore, the mortalities in the fish batch were below 5 % and the fish batch was accepted. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Hardness:
- 2.5 mmol/L (= 250.0 mg/L) as CaCO3
- Test temperature:
- 15 °C
- pH:
- 7.8 to 8.2
- Dissolved oxygen:
- 93 to 98 % of the air saturation value
- Nominal and measured concentrations:
- A filtrate of a supersaturated stock suspension of nominal 100 mg/L. No measured concentrations are available (below LOD).
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 12 litre glass aquaria with 10 litre test medium
- Aeration: The test media were slightly aerated during the test.
- No. of organisms per vessel: 7
- No. of vessels per concentration: 1
- No. of vessels per control : 1
TEST MEDIUM / WATER PARAMETERS
- Chlorine: 2.0 mmol/L (= 294.0 mg/L)
- Alkalinity: 0.8 mmol/L
- Ca/mg ratio: 4 : 1 (based on molarity)
- Conductivity: < 10 µS.cm-1
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH:
- Photoperiod: 16 h light : 8 h dark; 30 min dawn/dusk period was provided
- Light intensity: 780 to 810 lux
TEST CONCENTRATIONS
- Test concentrations:
The test item was not well soluble in test water. Therefore, a stock suspension of 100 mg test item/L was prepared by suspending 1.0002 g of test item in 10.0002 L test water for preparing the test concentration. The stock suspension was stirred for 24 hours to dissolve as much test item as possible. Then, the undissolved test item was separated by filtration (0.45 µm cellulose acetate nitrate filter). The test media were prepared just before introduction of the test fish (= start of the test). - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: up to the water solubility of the test item no mortality of the test animals occurred.
- Duration:
- 96 h
- Dose descriptor:
- LC0
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: up to the water solubility of the test item no mortality of the test animals occurred.
- Details on results:
- - Test item group: In the control and the only test concentration of nominal 100 mg test item/L, all fish survived until the end of the experiment and showed no sublethal effects during the exposure time.
- Control: In the control no fish died until the end of the test. - Sublethal observations / clinical signs:
Table 1 Mortality and Sublethal Effects
Nominal conc. [mg/L]
Exposure Time [h]
Control
100
0 h
# mort
0
0
# symp
0
0
symp
-
-
2 h
#mort
0
0
# symp
0
0
symp
-
-
24 h
#mort
0
0
# symp
0
0
symp
-
-
48 h
#mort
0
0
# symp
0
0
symp
-
-
72 h
#mort
0
0
# symp
0
0
symp
-
-
96 h
#mort
0
0
# symp
0
0
symp
-
-
# mort: Number of dead fish
# symp: Number of fish with sublethal effects
Table 2 Results for the Determination of the Test Item in the Test Samples
sample description
age
test item
found
[µg/L]
D.F.
calculated
test item
[µg/L]
day
[h]
control
0
0
<LOD
1000
n.a.
control
4
96
<LOD
1000
n.a.
Filtrate of 100 mg test item/L
0
0
<LOD
1000
n.a.
Filtrate of 100 mg test item/L
0
0
<LOD
1000
n.a.
Filtrate of 100 mg test item/L
4
96
<LOD
1000
n.a.
Filtrate of 100 mg test item/L
4
96
<LOD
1000
n.a.
LOD: Limit of Detection = 1.6 µg test item/L
n.a.: not applicable
D.F.: Dilution factor- Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the test results the 96-hour LC50 of potassium hexadecyl hydrogen phosphate for rainbow trout (Oncorhynchus mykiss) was determined to be higher than 100 mg test item/L (nominal). The LC0 was determined to be 100 mg test item/L (nominal).
- Executive summary:
The study was performed in order to evaluate the toxic potential of potassium hexadecyl hydrogen phosphate towards freshwater fish. The study was conducted as limit test in accordance with OECD TG 203 and Regulation (EC) No 440/2008 method C.1. Seven juvenile rainbow trout were exposed in a static test for 96 hours to test water containing the test item at the concentration of nominal 100 mg test item/L. As the test item is poorly water soluble, the “water-accommodated fraction” (WAF) was tested. Therefore, a stock suspension of 100 mg test item/L was prepared. The stock suspension was stirred for 24 hours to dissolve as much test item as possible. Then, the undissolved test item was separated by filtration. The test media were prepared just before introduction of the test fish. In the control and the only test concentration of nominal 100 mg test item/L, all fish survived until the end of the experiment and showed no sublethal effects during the exposure time. The pH and the oxygen values were in normal ranges. The 96-h LC50 was determined at greater than 100 mg/L and the 96-h LC0 was 100 mg/L.
Reference
Description of key information
Based on the test results the 96-hour LC50 of Potassium hexadecyl hydrogen phosphate for rainbow trout (Oncorhynchus mykiss) was determined to be higher than 100 mg test item/L (nominal). The LC0 was determined to be 100 mg test item/L (nominal).
Key value for chemical safety assessment
Additional information
The study was performed in order to evaluate the toxic potential of potassium hexadecyl hydrogen phosphate towards freshwater fish. The study was conducted as limit test in accordance with OECD TG 203 and Regulation (EC) No 440/2008 method C.1. Seven juvenile rainbow trout were exposed in a static test for 96 hours to test water containing the test item at the concentration of nominal 100 mg test item/L. As the test item is poorly water soluble, the “water-accommodated fraction” (WAF) was tested. Therefore, a stock suspension of 100 mg test item/L was prepared. The stock suspension was stirred for 24 hours to dissolve as much test item as possible. Then, the undissolved test item was separated by filtration. The test media were prepared just before introduction of the test fish. In the control and the only test concentration of nominal 100 mg test item/L, all fish survived until the end of the experiment and showed no sublethal effects during the exposure time. The pH and the oxygen values were in normal ranges. The 96-h LC50 was determined at greater than 100 mg/L and the 96-h LC0 was 100 mg/L.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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