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EC number: 219-006-1 | CAS number: 2312-35-8
- 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
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1st December 1983 to 22nd December 1983
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- according to guideline
- Guideline:
- other: ASTM (1981) E-47.01 and US EPA (1975) EPA_660/3-75-009
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Exposure concentrations of Omite were measured analytically on days 0, 4, 7, 14 and 21. The mean measured exposure levels were determined by gas chromatography.
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): acetone - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: Analytical Biochemistry Laboratories, Inc., Columbia, MO 65205, USA
- Age of parental stock (mean and range, SD): <24 hours old
- Feeding during test: yes
- Food type: an algal (Selenastrum capricornutum) suspension and a trout chow suspension
- Amount: 20-30 mL of the algal suspension and 5 mL of the trout chow suspension
- Frequency: three times daily for the algal suspension and once daily for the trout chow suspension - Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Test temperature:
- 20-21 ºC
- pH:
- 8.1-8.4
- Dissolved oxygen:
- 7.5-9.4 mg/L
- Nominal and measured concentrations:
- 0, 3.3, 6.0, 12, 22 and 50 µg/L (nominal)
0, 2.5, 4.1, 9.0, 14 and 38 µg/L (measured) - Details on test conditions:
- TEST SYSTEM
- Test vessel: 1 L test beakers
- Type (delete if not applicable): open (with stainless steel mesh)
- Type of flow-through: proportional diluter
- Renewal rate of test solution (frequency/flow rate): 4 times in a 24 hour period
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Metals: up to 0.056 ppm
- Alkalinity: 368 ppm
- Conductivity: 500 µmhos/cm
EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- Number of young three times a week; adult length at termination of study.
VEHICLE CONTROL PERFORMED: yes - Reference substance (positive control):
- no
- Key result
- Duration:
- 21 d
- Dose descriptor:
- other: MATC
- Effect conc.:
- > 9 - < 14 µg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- - Mortality of parent animals: survival from 38 µg/L was significantly different from the controls
- No. of offspring produced per day per female: 6.1-6.4
- Body length and weight of parent animals: Daphnid lengths from 14 µg/L were significantly different from the controls; length analysis from 38 µg/L could not be performed since no adults survived to 21 days - Reported statistics and error estimates:
- Statistical analysis
Adult length (pooled), survival and total young/adult/reproduction day were subjected to one way analysis of variance. When treatment effects were indicated following a significant F-test of the mean square ratios, a multiple means comparison test, Fisher's protected Least Significant Difference test (LSD) was used to determine which exposure levels differed from the controls.
Percent survival data were transformed for analysis using the following equation:
Angle = 2 arcsin √(X/N)
where:
X = number of organisms started with
N = number of organisms surviving to day 21
Total young/adult/reproduction day for each replicate was calculated as:
Total number of young produced / Total number of adult reproduction days - Validity criteria fulfilled:
- not specified
- Conclusions:
- Under the conditions of the test, propargite had no effect on survival or reproduction at concentrations up to 14 µg/L. However, this concentration caused a significant reduction in adult length. There was no effect on adult length at concentrations up to 9 µg/L. Therefore the NOEC, LOEC and MATC values were estimated to be 9, 14 and 9-14 µg/L, respectively.
- Executive summary:
A 21 day life cycle toxicity study of Omite® to Daphnia magna was conducted to determine the Maximum Acceptable Toxicant Concentration limits. A 0.5 L proportional diluter system was used to maintain constant test concentrations. Exposure concentrations of Omite® were measured analytically on days 0, 4, 7, 14 and 21. The mean measured concentrations determined by GC were 2.5, 4.1, 9.0, 14 and 38 µg/L. The mean measured exposure levels remained consistent throughout the study and all results were based on these values.
The daphnid lengths at 14 µg/L were significantly different from the control. Length analysis of the 38 µg/L concentration could not be performed since no adults survived after 21 days. Statistical analysis of survival indicated that 38 µg/L was significantly different from the control. The mean young/adult/reproduction day was significantly affected at 38 µg/L.
Based on the statistical analysis of adult mean length, survival and young/adult/reproduction day, the MATC limits were estimated to be 9 and 14 µg/L.
Reference
Table 1: Percent survival, young/adult/reproduction day and adult length
Concentration (µg/L) | Adult mean length (mm) | Mean percent survival | Mean young/adult/reproduction day | |
Control | 3.5 ± 0.13 | 82 ± 15 | 6.2 ± 0.55 | |
Solvent control | 3.5 ± 0.12 | 95 ± 10 | 6.5 ± 0.31 | |
2.5 | 3.5 ± 0.13 | 92 ± 9.6 | 6.4 ± 0.32 | |
4.1 | 3.5 ± 0.13 | 85 ± 17 | 6.1 ± 0.60 | |
9.0 | 3.5 ± 0.16 | 95 ± 5.8 | 6.4 ± 0.49 | |
14 | 3.4 ± 0.13 | 95 ± 5.8 | 6.3 ± 0.28 | |
38 | * | 0 | 0 |
*no adult survivors
Description of key information
MATC 9-14 µg/L; study conducted in accordance with ASTM (1981) E-47.01 and US EPA (1975) EPA_660/3-75-009; Forbis and Frankin, 1984
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 9 µg/L
Additional information
A 21 day life cycle toxicity study of propargite to Daphnia magna was conducted to determine the Maximum Acceptable Toxicant Concentration limits. A 0.5 L proportional diluter system was used to maintain constant test concentrations. Exposure concentrations of propargite were measured analytically on days 0, 4, 7, 14 and 21 and mean measured concentrations determined to be 2.5, 4.1, 9.0, 14 and 38 µg/L. The mean measured exposure levels remained consistent throughout the study and all results were based on these values.
The daphnid lengths at 14 µg/L were significantly different from the control. Length analysis of the 38 µg/L concentration could not be performed since no adults survived after 21 days. Statistical analysis of survival indicated that 38 µg/L was significantly different from the control. The mean young/adult/reproduction day was significantly affected at 38 µg/L. Based on the statistical analysis of adult mean length, survival and young/adult/reproduction day, the MATC limits were estimated to be 9 and 14 µg/L.
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