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EC number: 202-796-7 | CAS number: 99-87-6
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- June 1999
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 301 F
- Deviations:
- no
- Principles of method if other than guideline:
- Toxicity control used in OECD Guidelines for Testing of Chemicals, Method No. 301F
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on test solutions:
- The water used in the study was deionised water containing <10 mg/l dissolved organic carbon.
Mineral medium preparation
Stock solution A, made up to 1 litre of water:
KH2PO4: 8.5 g
K2HPO4: 21.75 g
Na2HPO4.2H2O: 33.4 g
NH4Cl: 0.5 g
Stock solution B, made up to 1 litre of water:
CaCl: 27.5 g
Stock solution C, made up to 1 litre of water:
MgSO4.7H2O: 22.5 g
Stock solution D, made up to 1 litre of water:
FeCl3.6H2O: 0.25 g
HCl conc.: one drop
Prepared by mixing 50 ml of solution A and 2000 ml deionised water and adding 5 ml of each of solutions B, C and D. The pH is measured and if necessary adjusted to 7.4+-0.2 with phosphoric acid or potassium hydroxide.
Two replicate 250 ml flasks were filled with 250 ml of mineral medium and the following test solution concentrations:
- test substance at a concentration of 100 mg/l;
- positive control or reference substance (sodium benzoate) at a concentration of 100 mg/l; and
- control blank.
A volume of suspended sludge corresponding to 7.5 mg dry weight was then added to each flask. The pH of the resulting test solution was only then measured if the test substance is of acid of alkaline character, if not measured then the pH was assumed to be the same as the mineral medium. Neutral test substances such as sodium benzoate do not tend to alter the pH of the test solution by more than 0.1 pH unit. About 2 g of soda lime is place in the attachment of the stopper and the flasks are closed and place in the water bath of the SAPROMAT. After temperature and pressure equilibration, the oxygen meters of the instrument are set to zero (time zero of the experiment).
Oxygen consumption was recorded daily alongside temperature and stirrer checks. At the end of the test the pH is measured again.
A concurrent study examining the toxicity of the test substance to the inoculum was conducted according to the OECD 301 F technical guidance. Two replicate 250 ml flasks were filled with 250 ml of mineral medium and the test substance and the reference substance (sodium benzoate), at concentrations of 100 mg/l each. These were incubated alongside the other test items and had their daily oxygen consumption readings recorded. If the daily oxygen readings of these flasks were below that of the positive control/reference substance then the test chemical can be assumed to be inhibitory to the inoculum used. - Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City of Geneva Aire) was used. The sludge is collected in the morning, washed 3 times in the mineral medium (centrifuging at 1000g for 10 minutes, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.
The dry weight and suspended solids is determined by taking 50 ml samples of the homogenised sludge, evaporating the water on a steam bath, drying in an oven at 105-110 °C for two hours and weighing the residue.
Activated sludge dry weight = 2.421 g/l - To obtain a concentration of 30 mg/l (dry weight) in a 250 ml flask, 3.1 ml of sludge was required. - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 28 d
- Test temperature:
- 22°C
- pH:
- initial pH: 7.5
- Nominal and measured concentrations:
- Nominal concentrations
- test substance: p-cymene100 mg/l
- reference substance : sodium benzoate 100 mg/l - Details on test conditions:
- Two replicate 250 ml flasks were filled with 250 ml of mineral medium and the following test solution concentrations:
- test substance at a concentration of 100 mg/l;
- positive control or reference substance (sodium benzoate) at a concentration of 100 mg/l; and
- control blank.
A volume of suspended sludge corresponding to 7.5 mg dry weight was then added to each flask. The pH of the resulting test solution was only then measured if the test substance is of acid of alkaline character, if not measured then the pH was assumed to be the same as the mineral medium. Neutral test substances such as sodium benzoate do not tend to alter the pH of the test solution by more than 0.1 pH unit. About 2 g of soda lime is place in the attachment of the stopper and the flasks are closed and place in the water bath of the SAPROMAT. After temperature and pressure equilibration, the oxygen meters of the instrument are set to zero (time zero of the experiment).
Oxygen consumption was recorded daily alongside temperature and stirrer checks. At the end of the test the pH is measured again.
A concurrent study examining the toxicity of the test substance to the inoculum was conducted according to the OECD 301 F technical guidance. Two replicate 250 ml flasks were filled with 250 ml of mineral medium and the test substance and the reference substance (sodium benzoate), at concentrations of 100 mg/l each. These were incubated alongside the other test items and had their daily oxygen consumption readings recorded. If the daily oxygen readings of these flasks were below that of the positive control/reference substance then the test chemical can be assumed to be inhibitory to the inoculum used. - Reference substance (positive control):
- yes
- Remarks:
- Sodium benzoate
- Key result
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other:
- Remarks:
- Inhibition of biodegradation of reference substance
- Details on results:
- The oxygen consumption curves for the reference substance alone and the reference substance plus p-cymene showed no toxic effects to the micro-organisms at the test concentration (100 mg/l nominal).
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The oxygen consumption curves for the reference substance alone and the reference substance plus p-cymene showed no toxic effects to the micro-organisms at the test concentration (100 mg/l nominal).
Reference
Description of key information
The oxygen consumption curves for the reference substance alone and the reference substance plus p-cymene showed no toxic effects to the micro-organisms at the test concentration (100 mg/l nominal).
Key value for chemical safety assessment
- EC50 for microorganisms:
- 100 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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