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EC number: 206-016-6 | CAS number: 287-92-3
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- August 1, 2003 - September 4, 2003
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant, guideline test. Available as an unpublished report, acceptable without restriction.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): Clinton Sanitary Wastewater Treatment Plant, Annandale, New Jersey
Activated sludge homogenised in blender (2 minutes, low speed). Allowed to settle for 60 minutes. Supernatant decanted. Supernatant, plus mineral asalt solutions, added to glass distilled water. Test medium aerated with CO2-free air for approximately 24 hours before test.
- Concentration of sludge: 10 mL sludge supernatant per liter of glass distilled water
- Mineral salt solutions (volumes per litre of glass distilled water):
-- 2.25% Magnesium sulphate solution: 1 mL/L
-- 2.75% Calcium chloride solution: 1 mL/L
-- pH 7.2 Phosphate buffer solution: 10 ml/L
-- 0.025% Ferric chloride solution: 1 mL/L
- Initial cell/biomass concentration: Microbal activity determined to be 100000 CFU/mL - Duration of test (contact time):
- 28 d
- Initial conc.:
- 50.31 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Activated sludge supernatant plus minteral salts in glass distilled water
- Test temperature: 22 ± 1°C
- pH: 7.28
- pH adjusted: Buffer solution present
- Suspended solids concentration: 3.61 g/L
TEST SYSTEM
- Culturing apparatus: One litre respirometer flask
- Number of culture flasks/concentration: 3
- Method used to create aerobic conditions: Aeration prior to test
- Measuring equipment: Manometric respirometer
- Test performed in closed vessels: yes
- Details of trap for CO2 and volatile organics if used: 10N NaOH as CO2 trap. Pressure reduction caused, triggering eletrolytic generation of O2 (measured with CES aerobic respirometer)
SAMPLING
none
CONTROL AND BLANK SYSTEM
Blank control and Sodium benxoate (postive control)
STATISTICAL METHODS:
Biodegration evaluation based on ThOD calculation. - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- at 50.69 mg/L
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 0
- Sampling time:
- 28 d
- Results with reference substance:
- 93.00 (SD: 4.40) % degradation after 28 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The test substance was not found to be biodegradable under the test conditions.
- Executive summary:
In a GLP, OECD 301F guideline test the test substance was found to undergo 0% biodegradation after 28. The test fulfilled the validity criteria. The test substance was not found to be biodegradable under the test conditions.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant, near guideline study, available as unpublished report, minor restrictions in design but otherwise adequate for assessment
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- yes
- Remarks:
- Deviations: The test medium was aerated for 18 hours with CO2 free air for homogeneity instead of 24 hours and the activated sludge was homogenized for 3 minutes instead of 2 minutes. The protocol deviations were not believed to to have adversly affected
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not reported - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, non-adapted
- Details on inoculum:
- Fresh activate sludge was used as the inoculum, obtained from the Somerset-Raritan Valley sewage authority in Bridegewater, New Jersey. Domestic sewage treatment works, no known contaminants believed to be present.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 60 mg/L
- Based on:
- ThOD/L
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Test was conducated according to OECD guideline 301F. Test material was evaluated in triplicate test systems at a concentration of approximately 60 mg/l. The amount of oxygen taken up by the microbial populations during biodegradation of the test material, corrected for uptake by blank inoculum) is expressed as a percentage of ThOD. Biodegradation of the sodium benzoate was also measured. Duplicate blank test systems, which did not contain the test or positive control were run at the same time.
- Reference substance:
- benzoic acid, sodium salt
- Test performance:
- Test is considered valid since sodium benzoate biodegraded to approximately 97 % by day 14 and so fullfilled the guideline requirement of > 60% biodegradation within the 1st 14 days.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 3
- St. dev.:
- 0.4
- Sampling time:
- 7 d
- Remarks on result:
- other: Based on ThOD
- Parameter:
- % degradation (O2 consumption)
- Value:
- 48.8
- St. dev.:
- 2.2
- Sampling time:
- 11 d
- Remarks on result:
- other: Based on ThOD
- Parameter:
- % degradation (O2 consumption)
- Value:
- 65.5
- St. dev.:
- 1.7
- Sampling time:
- 13 d
- Remarks on result:
- other: Based on ThOD
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 87
- St. dev.:
- 4.2
- Sampling time:
- 28 d
- Remarks on result:
- other: Based on ThOD
- Details on results:
- Biodegradation was calcualted as the net amount of oxygen (mg) consumed by the test system multiplied by a constant. Net amount of oxygen was calculated as the difference between the test system oxygen consumption (mg) and the average oxygen oxygen (mg) consumed by the blanks
- Results with reference substance:
- 97 % biodegradation of sodium benzoate occured by day 14.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- 87 % of initial n-pentane degraded in 28 days. N-pentane is therefore readily biodegradable
- Executive summary:
The test was considered valid as 97 % degradation of sodium benzoate occured by day 14 and n-pentane was shown to be readily biodegradable with 87 % biodegradation occuring within 28 days.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- April 5th 1996 - May 3rd 1996
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study was non-GLP and non guideline, minor restrictions in design abut otherwise adequate for assessment
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Principles of method if other than guideline:
- Study design was based on OECD Guideline for Testing of Chemicals, Method 301F Manometric Respirometry Test. One notable deviation from the guideline was the concentration of the test substance, which was less than the range stated in the guideline but from calculation of the ThOD for isopentane (based on OECD 301F equation) the range used was still deemed suitable. Triplicate test systems were used for the test substance and duplicates used for the control material and the blank controls.
- GLP compliance:
- no
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not reported - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Inoculum used as the source of microorganisms was an aliquot of fresh activated sludge obtained from domestic sewage works.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 25 - 33 mg/L
- Based on:
- ThOD/L
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Study design was based on OECD Guideline for Testing of Chemicals, Method 301F Manometric Respirometry Test. One notable deviation from the guideline was the concentration of the test substance, which was less than the range stated in the guideline but from calculation of the ThOD for isopentane (based on OECD 301F equation) the range used was still deemed suitable. Triplicate test systems were used for the test substance and duplicates used for the control material and the blank controls.
- Reference substance:
- benzoic acid, sodium salt
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 71.43
- Sampling time:
- 28 d
- Details on results:
- The study was similar to OECD Method 301F Manometric respirometry test. The details of the ThOD of the subtance was not reported and so the suitablity of the test concentration was not clear for the report. However calculation of the ThOD of isopentane (3.6 mg/mg), using the standard equation in Annex IV of the method, did show that the concentration used did meet the criteria of at least 50 -100 mg ThOD/L specified in the guideline. % biodegradation varied between the individual replicates by >20%. However as all replicates exceeded 60 % of ThOD within the 28 day period, isopentane can be considered readily biodegradable
- Results with reference substance:
- Sodium benzoate: Initial concentration 51 mg/L. >60% degradation by day 14 so test could be considered valid
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- 71.43 % degredation occured within 28 days and so 2-methylbutane is considered to be readily biodegradable.
- Executive summary:
This followed the OECD guideline 301F manometric respirometry test with some minor deviations in test concentrations. However this deviation from the guideline were shown to not affect the integrity of the study as it meet the validity criteria. The study was therefore deemed suitable for assessment. This study indicates that isopentane is readily biodegradable.
Referenceopen allclose all
Description of key information
There is data available for this substance. Additionally, key data is available for the structural analogues Pentane and 2-methylbutane and is presented in the dossier. The data is read across to this substance based on analogue read across and a discussion and report on the read across strategy is provided as an attachment in IUCLID Section 13.
Based on the available data, this substance is considered readily biodegradable. Key information is summarised below:
Pentane biodegraded 87% after 28 days under the conditions of the study and is therefore considered readily biodegradable.
2 -methylbutane biodegraded 71.43 % after 28 days under the conditions of the study and is therefore considered readily biodegradable.
Cyclopentane biodegraded 0% after 28 days under the conditions of the study and is therefore considered not biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
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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