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EC number: 222-048-3 | CAS number: 3327-22-8
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2004-08-11 to 2004-09-01
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to the appropriate OECD test guideline, and in compliance with GLP. Analytical monitoring was also conducted.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- (3-chloro-2-hydroxypropyl)trimethylammonium chloride
- EC Number:
- 222-048-3
- EC Name:
- (3-chloro-2-hydroxypropyl)trimethylammonium chloride
- Cas Number:
- 3327-22-8
- Molecular formula:
- C6H15ClNO.Cl
- IUPAC Name:
- 3-chloro-2-hydroxy-N,N,N-trimethylpropan-1-aminium chloride
- Details on test material:
- - Name of test material (as cited in study report): (3-chloro-2-hydroxypropyl)trimethylammonium chloride / 65.2 %
- Physical state: yellowish clear liquid
- Stability under test conditions: stability in water 641 h @ pH 7, 25 degC; <1 d @ pH 9, 25 degC. water solubility = 835 g/L
- Storage condition of test material: room temperature, protected from moisture and light.
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: The concentrations of CHPTAC and its conversion product 2,3-Epoxypropyltrimethylammonium chloride (EPTAC) were determined via HPLC/MS MS in all test item concentrations (0.17, 0.51, 1.52, 4.56, 13.7 mg/l) and controls.
- Sampling method: Samples were taken on days 0, 7, 14, 19 (fresh media) and days 2, 9, 16, 21 (old media).
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: a stock solution of 100 mg/L (i.e. 65.2 mg/L of the active ingredient CHPTAC) is said to be dispersed by agitation. No further details on the preparation of the test solution are reported. Given the high water solubility of the test substance it is assumed by the reviewer that either serial dilutions of the stock solution were made with test medium as dilution water, or that the test substance was added to the test medium to achieve the nominal concentrations desired.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Clone: 5
- Source: the test organisms were bred at the testing facility, origin Insitut fur Wasser-, Boden- und Lufthygiene (WaBoLu).
- Age of parental stock (mean and range, SD): 2-24 h old, the test organisms were not the first brood progeny.
- Feeding during test
- Food type and amount: The food quantity was a D. subspicatus (0.395 - 1.45 mL) and C. vulgaris (0.375- 0.745 mL) suspension of algae per test vessel (corresponding to 0.1 - 0.2 mg C per Daphnia per day). lt varied according to the growth of the daphnids, but was the same for all test groups on any particular day.
- Frequency: At lest 5 times per week.
ACCLIMATION
- Acclimation conditions: the test organisms were bread in an incubator in similar conditions to the test (temperature, illumination and photoperiod), in 2-3 L glass vessels with approx. 1.8 L culture medium.
- Type and amount of food: a mix of D. subspicatus and C. vulgaris with algae cell density of >10^6 cells/ml ad libitum.
- Feeding frequency: at least 5x per week
- Health during acclimation: the stock population is defined as healthy by the authors of the report.
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
Test conditions
- Hardness:
- total hardness > 140 mg/L as CaCO3
- Test temperature:
- range: 20.3 to 21.6 degC
- pH:
- The initial pH values varied from 7.85 to 8.75 at 1.52 and 13.7 mg a.i./L, respectively and from 8.06 to 8.61 in the control. The final pH values varied from 7.55 to 7.73 at 1.52 mg a.i./L, from 8.4 to 8.9 at 13.7 mg a.i./L and from 7.71 and 8.58 in the control.
- Dissolved oxygen:
- The final oxygen concentrations of the measured replicates in the test media of nominal 1.52, 13.7 mg a.i./L and control were found to be greater than or equal to 7.64 mg/L.
- Nominal and measured concentrations:
- Nominal concentrations (test item): 0.26, 0.78, 2.33, 7.00, 21.0 mg/L
Nominal concentrations (active ingredient, a.i.): 0.17, 0.51, 1.52, 4.56, 13.7 mg a.i./L - Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Material, size, headspace, fill volume: glass beakers (5 (ID) x 8 (h) cm), 100 ml filled with 50 ml test solution.
- Renewal rate of test solution (frequency): 3 times per week
- No. of organisms per vessel: 1
- No. of vessels per concentration (replicates): 10
- No. of vessels per control (replicates): 10
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt M4, according to Elendt (1990), modified to a total hardness of 160-180 mg/L as CaCO3
- Total organic carbon: 1.44 mg/L
- Particulate matter: <0.1 mg/L
- Metals: within acceptable ranges
- Pesticides: <0.025 ug/L
- Chlorine: <0.003 mg/L
- Conductivity: <0.1 uOhm
- Culture medium different from test medium: culture medium - Elendt M4, according to Elendt (1990), modified to a total hardness of 160-180 mg CaCO3/L
- Intervals of water quality measurement: Dissolved oxygen concentration, pH, total hardness and water temperature were measured once a week, in fresh and old media, in one replicate of the control and the highest concentration of the test item.
OTHER TEST CONDITIONS
- Photoperiod: 16h/8h light/dark cycle
- Light intensity: max 20 uE /m^2/s
EFFECT PARAMETERS MEASURED:
o mortality of parent daphnia - measured once per day
o newborn offspring first appearance - daily;
o number of live and dead offspring - daily;
o aborted eggs - daily;
o abnormalities of parent daphnia - each day of observation;
o body length and weight (parent daphnia) - end of test.
RANGE-FINDING STUDY
- Test concentrations: two separate range finding studies: 1.0-1000 mg/L
- Results used to determine the conditions for the definitive study: 100 and 20% immobilisation at 1000 and 100 mg/L respectively. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.51 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 1.52 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- EC50
- Effect conc.:
- 1.52 - 4.56 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Details on results:
- - Mortality of parent animals: 100% mortality occurred at 13.7 and 4.56 mg a.i./L treatments and 60% mortality at 1.52 mg a.i./L after 21 days.
- Body length and weight of parent animals: see Table 1 for details. No statistical analysis was applied to these parameters.
- Time to first brood release or time to hatch: no statistically significant difference between treatment levels and the control.
- Brood size: At 1.52 mg/l the reproduction output was significantly higher than in controls or other test groups indicating a stress reaction. No significant reduction in reproduction compared to the control was not observed at lower concentration levels. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Relevant effect levels: 24 h EC50 value of 1.94 mg/L - Reported statistics and error estimates:
- The EC50 value for immobilisation of parent daphnia was calculated by probit analysis (Weber 1986) was calculated by probit analysis. While the NOEC was and LOEC for the a.i. CHPTAC for the reproduction were determined directly from the results.
Any other information on results incl. tables
Table 1: Effect of test material on growth and survival of D. magna (average per 10 replicates unless otherwise stated) during the 21 day test.
Treatment (mg a.i./L) nominal concentration |
Mortality of parents (dead or immobile) |
Mean no. of offspring |
No. of juveniles per parent alive (mean ± SD) |
Day of first appearance of juveniles |
Mean length (mm) |
Mean weight (mg) |
|
No. Dead (per 10 replicates) |
% (per 10 replicates) |
||||||
Control |
1 |
10 |
970 |
108 ± 5.04 |
7.1 |
5.39 |
1.27 |
13.7 |
10 |
100 |
- |
0 ± 0 |
8 |
- |
- |
4.56 |
10 |
100 |
- |
0 ± 0 |
8 |
- |
- |
1.52 |
6 |
60 |
520 |
130 ± 13 |
8 |
5.44 |
0.55 |
0.51 |
1 |
10 |
960 |
107 ± 11.3 |
7.4 |
5.53 |
1.01 |
0.17 |
0 |
0 |
1063 |
106 ± 8.54 |
7.1 |
5.45 |
1.18 |
- denotes when an endpoint is not applicable, e.g. the parent daphnia died before the end of the test and it was not possible to measure length and weight.
Table 2: Parental daphnia immobilisation results.
Endpoint |
Result (mg a.i./L, nominal) |
NOEC |
1.03 |
LOEC |
1.52 |
EC50 |
0.51 |
Table 3: Nominal and measured concentrations (ranges) during exposure.
|
|
Measured concentration (mg a.i./L) results |
|||||
Nominal concentration |
0 (control) |
13.7 |
4.56 |
1.52 |
0.51 |
0.17 |
|
Fresh media |
CHPTAC range (min.-max.) |
< LOQ |
13.1 |
4.65-4.87 |
1.41-1.52 |
0.477-0.542 |
0.158-0.19 |
EPTAC as CHPTAC range (min. - max.) |
<LOQ |
n.c. |
n.c. |
n.c. |
n.c. |
n.c. |
|
Sum range (min. - max.) |
<LOQ |
13.1 |
4.65-4.87 |
1.41-1.52 |
0.477-0.542 |
0.158-0.19 |
|
Old media (48 h) |
CHPTAC range (min.-max.) |
<LOQ |
8.8 |
3.06-3.22 |
1.08-1.41 |
0.317-0.405 |
0.12-0.161 |
EPTAC as CHPTAC range (min. - max.) |
<LOQ |
3.91 |
1.31-1.37 |
0.107-0.459 |
0.134-0.179 |
0.0378-0.064 |
|
Sum range (min.-max.) |
<LOQ |
12.7 |
4.37-4.59 |
1.51-1.61 |
0.474-0.546 |
0.163-0.189 |
n.c. defines not calculable because concentrations measured for EPTAC were <LOQ.
Measurements were only taken where living test organisms were present so for higher treatment value are not representative of the whole 21 day exposure.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 21 day NOEC value of 0.51 mg a.i./L has been determined for the effects of the test substance on reproduction of the test organism D. magna.
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