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EC number: 951-169-0 | CAS number: -
- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- The study will be available 30/06/2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- no
- Principles of method if other than guideline:
- The solution of the test item in mineral medium is inoculated with a relatively small number of microorganisms from i mixed population and kept in completely full closed bottles in the dark at constant temperature.
Degradation is determined by analysis of dissolved oxygen over a 28-day period.
The following determinations were done simultaneously under the same conditions:
- check of inoculum activity with the reference item
- toxicity test of the test item for used inoculum in mixtrue of the test and reference item
- determination of ixygen consumption for nitrification
- determination of blank (inoculated mineral medium).
The amount of oxygen taken up by the test chemical, corrected for uptake by the blank inoculum run i parallel, is expressed as a percentage of ThOD.
ThOD (Theoretical oxygen demand (mg) is the total amount of oxygen required to oxidise a chemical completely; it is calculated from the molecular formula and it is also expressed as mg oxygen required per mg test compound. - GLP compliance:
- yes
Test material
- Reference substance name:
- 2-methylbutan-1-ol; 2-methylbutyl nitrite; pentan-1-ol; pentyl nitrite
- EC Number:
- 951-169-0
- Molecular formula:
- C15H46N2O10
- IUPAC Name:
- 2-methylbutan-1-ol; 2-methylbutyl nitrite; pentan-1-ol; pentyl nitrite
- Test material form:
- liquid
Constituent 1
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, predominantly domestic (adaptation not specified)
- Details on inoculum:
- THE PREPARATION OF INOCULUM
The inoculum contained a mixed population of microorganisms obtained from the secondary effluent of the waste water treatment plant of Pardubice processing predominantly minucipal sewage.
The fresh collected waste water was filtered through paper filter and aerated till using.
The inoculum preparation is in conformity with the recommendations of the test guideline.
The volume of waste water for the inoculation of mineral medium was chosen 1.8 mL per 1 L of medium. 30 L aerated mineral medium was prepared for the test and before the beginning of the test it was inoculated with 54 mL of modified waste water. The pH value of medium: 7.4 - Duration of test (contact time):
- ca. 28 d
Initial test substance concentration
- Initial conc.:
- ca. 2.91 - 3.05 mg/L
- Based on:
- ThOD
- Remarks:
- More information - Table 1 (Concentration of the test item in bottles)
Parameter followed for biodegradation estimationopen allclose all
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- for nitrification
- Parameter followed for biodegradation estimation:
- other: toxicity test of the test item for used inoculum in mixture of the test and reference item
- Parameter followed for biodegradation estimation:
- other: check of inoculum activity with the reference item
- Parameter followed for biodegradation estimation:
- other: determination of blank (inoculated mineral medium)
- Details on study design:
- TEST ITEM: The test item was weighed directly into bottle and the bottles were completed to the whole volume with inoculated medium. Mixtures prepared in this way contained 2.91 - 3.05 mg.L-1 of the test item.
REFERENCE ITEM: The stock solution of sodium benzoate was prepared in concentration 1.0000 g.L-1 of deionized water. From this solution the 12.6 mL (2.1 mL.L-1) were transfered to a large glass bottle and completed with the inoculated medium to the volume of 6 L. The solution preparad in this wqy contained 2.10 mg.L-1 of sodium benzoate. The pH value of solution: 7.5
TOXICITY TEST: The test item was weighed directl into bottle and the bottles were completed to the whole volume with inoculataed solution of sodium benzene. The mixture prepared in this way contained 2.91 - 3.06 mg.L-1 of the test item (Table 2) and 2.10 mg.L-1 of sodium benzoate.
TEST CONDITIONS Exposition time: 28 days
Temperature: 20 ± 1 °C
Illumination: no illumination, in the dark
TEST DESIGN
The number of bottles for individual series:
Test item series: 2 x 9 bottles with test item and inoculum
Reference item series: 2 x 9 bottles with reference item and inoculum
Blank series: 2 x 9 bottles with inoculated medium only
Series for nitrification determination: 1 x 9 bottles with test item and inoculum
Toxicity test series: 2 x 5 bottles with test item, reference item and inoculum
The prepared dosing solutions for each series were filled in two parallel bottle replicates (except the series for nitrification determination) . The bottles were placed into thermostat.
MEASUREMENTS: The first two bottles from each series were immediately submitted to analysis for dissolved oxygen (zero-time) and other bottles are placed in the thermostat.
On the 3rd, 7th, 10th, 14th, 17th, 21st, 24th and 28th day of the test, two bottles (parallel replicate) from the test item series, from the reference item series, from the blank series and one bottle from series for nitrification determination were taken off and the determinations were performed.
On the 3rd, 7th, 10th, 14th day of the test, two bottles from the toxicity test series were taken off and the determinations was performed.
The analysis of dissolved oxygen was performed electrochemically using oximeter dievice (oximeter WTW OXI 730).
On the 3rd, 7th, 10th, 14th, 17th, 21st, 24th and 28th day of the test, one bottle from the series for nitrification determination was taken off and stored in freezer. The determinations of nitrite-N concetration and nitrate-N concentration were carried out by ion chromatography at one time at the end of the test. These analyses were performed as GLP work.
Reference substance
- Reference substance:
- benzoic acid, sodium salt
Results and discussion
- Test performance:
- MEASUREMENTS: The first two bottles from each series were immediately submitted to analysis for dissolved oxygen (zero-time) and other bottles are placed in the thermostat.
On the 3rd, 7th, 10th, 14th, 17th, 21st, 24th and 28th day of the test, two bottles (parallel replicate) from the test item series, from the reference item series, from the blank series and one bottle from series for nitrification determination were taken off and the determinations were performed.
On the 3rd, 7th, 10th, 14th day of the test, two bottles from the toxicity test series were taken off and the determinations was performed.
The analysis of dissolved oxygen was performed electrochemically using oximeter dievice (oximeter WTW OXI 730).
On the 3rd, 7th, 10th, 14th, 17th, 21st, 24th and 28th day of the test, one bottle from the series for nitrification determination was taken off and stored in freezer. The determinations of nitrite-N concetration and nitrate-N concentration were carried out by ion chromatography at one time at the end of the test. These analyses were performed as GLP work.
% Degradation
- Key result
- Parameter:
- % degradation (DOC removal)
- Value:
- ca. 33.8
- Sampling time:
- 28 d
- Remarks on result:
- readily biodegradable based on QSAR/QSPR prediction
- Details on results:
- According to paragraph 10 of OECD TG 301 the pass level for ready biodegradability is 60% of ThOD values for respirometric methods.
BOD5 / COD results
BOD5 / COD
- Parameter:
- ThOD
- Value:
- ca. 2.185 other: mg.mg-1
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- In this 28-day study of ready biological degradability the degradation of 33.8 % of the test
item, Pentyl nitrite, was attained in the end of study. - Executive summary:
The test item , Pentyl nitrite, was tested for the ready biological degradability in Closed Bottle
Test.
Test performance
The test was performed according to:
Method C.4E - Closed Bottle Test, Council Regulation (EC) No. 440/2008, published
in O.J .L 142, 2008
OECD Test Guideline No. 301 D - Closed Bottle Test. Adopted July 17, 1992
The test item is non-soluble in the mineral medium. For these reasons the direct dosing of the
test item into each bottle was implemented.
Sodium benzoate was used as the reference item. The dosage was carried out from the stock
solution.
In parallel to the main test the toxicity test was performed.
Based on the test item contains nitrogen in the chemical composition , the oxidized nitrogen
forms were dete1mined and the correction for nitrification was carried out.
The test was performed at temperature of 20 ± I °C with the pH values of solutions 7 - 8
at the beginning of the test.
The calculations of biological degradation are based on ThOD (theoretical oxygen demand)
values of the test and reference item.
Validity of the test
The prescribed validity criteria in the test were fulfilled.
The test item was not inhibiting for the used inoculum.
Since all criteria of acceptability were met, this study is considered to be valid.
Test results
In this 28-day study of ready biological degradability the degradation of 33.8 % of the test
item, Pentyl nitrite, was attained in the end of study.
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