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EC number: 261-351-5 | CAS number: 58594-72-2
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Data from the related substance imazalil base is used to cover this endpoint. The justification for read across is attached in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 16 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 133 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- not indicated
- 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: Soap and Detergent Association, Test Procedure and Standards, ABS and LAS Biodegradability, J. 1M. Oil Chemists Soc. 42: 986-993
- Qualifier:
- according to guideline
- Guideline:
- other: Standard Methods for the examination of water and waste water, 13th Ed., 1971, APHA, AWWA & WPCF, New York
- Principles of method if other than guideline:
- - Principle of test:
The aim of the present study is to determine if imazalil is capable of disturbing the operation of a sewage treatment plant. For that purpose, a semi-continuous activated sludge metabolism study was carried out with imazalil following the Standard Method of the Soap and Detergent Association. - GLP compliance:
- not specified
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The method involves the daily addition of fresh synthetic sewage (1l) containing the test compound, to activated sludge (0.5l). The synthetic sewage was prepared daily. In order to acclimatize the sludge, imazalil concentration was gradually increased from 0.10 to 100.0 ppm imazalil, in a period of 9 days. The treatment with the final concentration 100.0 ppm was repeated four times.
- Composition of synthetic sewage (pro litre):
* 8.50 mg KH2PO4
* 21.75 mg K2HPO4
* 33.40 mg Na2HPO4.2H2O
* 1.70 mg NH4Cl
* 22.50 mg MgSO4.7H2O
* 27.50 mg CaCl2
* 0.25 mg FeCl3.6H2O
* 300.00 mg peptone
* 200.00 mg beef extract
* 70.00 mg urea - Test organisms (species):
- activated sludge
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 16 d
- Hardness:
- not indicated
- Test temperature:
- not indicated
- pH:
- not indicated
- Dissolved oxygen:
- not indicated
- Salinity:
- not applicable
- Conductivity:
- not applicable
- Nominal and measured concentrations:
- not applicable
- Details on test conditions:
- TEST SYSTEM
The method involves the daily addition of fresh synthetic sewage (1l) containing the test compound, to activated sludge (0.5l). The obtained mixture is aerated for 23 hours in a closed system; afterwards the sludge is allowed to settle for 30 minutes and then the supernatant (1l) is removed from the sludge unit. Fresh synthetic sewage and test compound are added again to the remaining sludge and the cycle is repeated.
The sludge unit was dosed daily with the synthetic sewage containing increasing concentrations of imazalil for 16 consecutive days. Dosing started at 0.10 ppm imazalil and increased up to 100.0 ppm.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Sewage COD reduction: Before each adding of the new synthetic sewage to the sludge unit, a small sample of the solution (about 5 ml) was taken for COD analysis (COD initial). At the end of each cycle, when sludge was completely settled, 1l of supernatant was removed and investigated for COD (COD final). The daily COD reduction is expressed as a difference between these two values.
- CO2-production of system: During each cycle the activated sludge system was aerated continuously and the produced CO2 trapped. During settling of the sludge after the 23 hours period, the whole CO2-trapping solution was removed and analyzed for CO2-content.
- Microbiological activity and solid content of water/sludge mixture: After each 23 hours (exceptionally 71 hours after week-ends) period of continuous aeration of the sludge unit, just before settling of the sludge, this mixture was sampled for determination of microbiological growth and concentration of solids in the sludge.
TEST CONCENTRATIONS
- Test concentrations: 0.10, 0.27, 0.72, 1.93, 5.18, 13.90, 37.28, 100 ppm imazalil in sewage solution - Reference substance (positive control):
- no
- Key result
- Duration:
- 16 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Duration:
- 16 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Details on results:
- Addition of imazalil up to 100.0 ppm did not seem to have reached the toxic limit as:
* COD reduction did not seem to be influenced,
* CO2-production remained stable,
* microbial growth, estimated by the Standard Plate Count Technique was not affected adversely,
* concentration of solids in the medium remained the same - Validity criteria fulfilled:
- yes
- Conclusions:
- The influence of Imazalil on the operation of a sewage treatment plant was analysed. After repeated tests with increasing concentrations up to 100 ppm of Imazalil on a bench scale activated sludge unit, it was clearly indicated that Imazalil has no toxic or inhibitory effect on the biomass.
Referenceopen allclose all
Description of key information
The study of Peeters et al. (1980), investigating the toxicity of Imazalil to STP microorganism, was considered as the key study for endpoint coverage. Addition of Imazalil up to 100 ppm did not reach the toxic limit which corresponds to 133 mg imazalil sulphate/L
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 133 mg/L
Additional information
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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