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EC number: 500-020-4 | CAS number: 9005-67-8 1 - 6.5 moles ethoxylated
- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: data is from peer reviewed journal
- Justification for type of information:
- data is from peer reviewed journal
- Qualifier:
- according to guideline
- Guideline:
- other: refer principle below
- Principles of method if other than guideline:
- Biodegradability of test chemical was determined by using methane production using mixed methanogenic culture for 82 days.
- GLP compliance:
- not specified
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- other: Methanogenic culture
- Details on inoculum:
- A contaminated sediment sample from the Bayou d’Inde, a tributary of the Calcasieu River near Lake Charles, Louisiana, was used as the inoculum for the development of mixed, methanogenic cultures. For decades, this tributary received discharges of industrial pollutants, including chlorinated compounds such as HCB and hexachlorobutadiene. Initially, two HCB-dechlorinating, methanogenic mixed cultures, one glucose fed and one lactate fed, were developed in anaerobic media containing mineral salts, nutrients, trace metals,
vitamins, and sodium sulfide to maintain highly reducing conditions. The stock cultures were maintained at 22oC in 9-L (6-L liquid volume), sealed glass reactors with a 14-d fill and- draw cycle, resulting in an average hydraulic (and solids) retention time of 84 d. During each feeding cycle (7–9 d), the cultures received 333 mg/L of the primary electron donor (glucose or lactate), yeast extract (17 mg/L), and HCB (0.027 mg/L via 0.4 ml of a 400-mg HCB/L methanol solution). The cultures were maintained at an oxidation-reduction potential (ORP) of 2330 6 10 mV, a pH of 6.9 to 7.1 (glucose-fed culture) or 7.2 to 7.5 (lactate-fed culture), and were sediment free at the time bioassays were conducted - Duration of test (contact time):
- 87 d
- Initial conc.:
- 200 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- other: Methane production
- Details on study design:
- Two batch assays were conducted to screen the test chemical for their effect on methanogenesis . Assay was performed using helium-flushed, 70-ml glass serum bottles (each containing 50 ml of liquid culture) sealed with thick butyl rubber stoppers and aluminum crimps (Wheaton, Millville, NJ, USA). All incubations took place in the dark at 22oC, and the bottles were shaken manually each day. For each assay, triplicate serum
bottles were prepared in three experimental series as follows:
(1) seed blank control (without any electron donor added);
(2)primary electron donors (either 1,800 mg/L glucose or 1,800
mg/L lactate plus 90 mg/L yeast extract) as reference; and
(3) primary electron donors and test chemical at 200 mg/L (0.33–0.42 g COD/L) - Parameter:
- other: Methane production
- Sampling time:
- 7 d
- Remarks on result:
- other: Methane produced by day 7 as a percentage of the total methane produced in 82 d of incubation
- Details on results:
- Methane produced by day 7 as a percentage of the total methane produced in 82 d of incubation was 52% by using methane production as Parameter in 7 days by using methanogenic culture lactate feed culture in anaerobic condition
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- inherently biodegradable
- Conclusions:
- Methane produced by day 7 as a percentage of the total methane produced in 82 d of incubation was 52% by using methane production as Parameter in 7 days by using methanogenic culture lactate feed culture in anaerobic condition. By considering this value test chemical was considered to be inherently biodegradable.
- Executive summary:
Two batch assays were conducted to screen the test chemical for their effect on methanogenesis . Assay was performed using helium-flushed, 70-ml glass serum bottles (each containing 50 ml of liquid culture) sealed with thick butyl rubber stoppers and aluminum crimps .All incubations took place in the dark at 22oC, and the bottles were shaken manually each day. For each assay, triplicate serum bottles were prepared in three experimental series as follows:
(1) seed blank control (without any electron donor added)
(2) primary electron donors (either 1,800 mg/L glucose or 1,800 mg/L lactate plus 90 mg/L yeast extract) as reference; and
(3) primary electron donors and test chemical at 200 mg/L (0.33–0.42 g COD/L)
The inoculum used was methanogenic cultures which was obtained from contaminated sediment sample from the Bayou d’Inde, a tributary of the Calcasieu River near Lake Charles, Louisian For decades, this tributary received discharges of industrial pollutants, including chlorinated compounds such as HCB and hexachlorobutadiene
After incubation Gas samples were removed from the culture headspace using a gas-tight syringe and analyzed for methane by gas chromatography.
Methane produced by day 7 as a percentage of the total methane produced in 82 d of incubation was 52% by using methane production as Parameter in 7 days by using methanogenic culture lactate feed culture in anaerobic condition. By considering this value test chemical was considered to be inherently biodegradable.
Reference
Description of key information
Two batch assays were conducted to screen the test chemical for their effect on methanogenesis . Assay was performed using helium-flushed, 70-ml glass serum bottles (each containing 50 ml of liquid culture) sealed with thick butyl rubber stoppers and aluminum crimps .All incubations took place in the dark at 22oC, and the bottles were shaken manually each day. For each assay, triplicate serum bottles were prepared in three experimental series as follows:
(1) seed blank control (without any electron donor added)
(2) primary electron donors (either 1,800 mg/L glucose or 1,800 mg/L lactate plus 90 mg/L yeast extract) as reference; and
(3) primary electron donors and test chemical at 200 mg/L (0.33–0.42 g COD/L)
The inoculum used was methanogenic cultures which was obtained from contaminated sediment sample from the Bayou d’Inde, a tributary of the Calcasieu River near Lake Charles, Louisian For decades, this tributary received discharges of industrial pollutants, including chlorinated compounds such as HCB and hexachlorobutadiene
After incubation Gas samples were removed from the culture headspace using a gas-tight syringe and analyzed for methane by gas chromatography.
Methane produced by day 7 as a percentage of the total methane produced in 82 d of incubation was 52% by using methane production as Parameter in 7 days by using methanogenic culture lactate feed culture in anaerobic condition. By considering this value test chemical was considered to be inherently biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable
Additional information
Experimental studies have been reviewed from different sources for test chemical to determine biodegradability of test chemical and their results are summarized below.
The first experimental study was reviewed from Environmental Toxicology Chemistry Journal (1999) in this study the Two batch assays were conducted to screen the test chemical for their effect on methanogenesis . Assay was performed using helium-flushed, 70-ml glass serum bottles (each containing 50 ml of liquid culture) sealed with thick butyl rubber stoppers and aluminum crimps .All incubations took place in the dark at 22oC, and the bottles were shaken manually each day. For each assay, triplicate serum bottles were prepared in three experimental series as follows: (1) seed blank control (without any electron donor added) (2) primary electron donors (either 1,800 mg/L glucose or 1,800 mg/L lactate plus 90 mg/L yeast extract) as reference; and (3) primary electron donors and test chemical at 200 mg/L (0.33–0.42 g COD/L) The inoculum used was methanogenic cultures which was obtained from contaminated sediment sample from the Bayou d’Inde, a tributary of the Calcasieu River near Lake Charles, Louisian For decades, this tributary received discharges of industrial pollutants, including chlorinated compounds such as HCB and hexachlorobutadiene .After incubation Gas samples were removed from the culture headspace using a gas-tight syringe and analyzed for methane by gas chromatography. Methane produced by day 7 as a percentage of the total methane produced in 82 d of incubation was 52% by using methane production as Parameter in 7 days by using methanogenic culture lactate feed culture in anaerobic condition. By considering this value test chemical was considered to be inherently biodegradable.
To support the results of above mentioned study another study was reviewed from Water Science technology Journal (1998)in this study Serum bottle assays were conducted to screen the test chemical for their ability to enhance or inhibit Methanogenesis to determine biodegradability of test chemical , were performed using He-flushed 70-mL glass serum bottles sealed with thick butyl rubber stoppers and aluminum crimps (Wheaton, Millville, NJ), each containing 50 mL culture. All incubation occurred in the dark at 22°C with the bottles shaken daily. The glucose-fed culture was used in the first serum bottle assay, while the lactate-fed culture was used in the second assay. Experimental series of serum bottles were prepared in triplicates as follows: seed blank (without any electron donor added) for control; primary electron donors (either 1800 mg/L of glucose or lactate, plus 90 mg/L yeast extract, to result in a loading of 1.92 g COD/L) for reference; primary electron donors amended with surfactant at 200 rug/L (0.33042 g COD/L) to assess the effect of test chemical on the methanogenesis rate and extent; and surfactant at 200 mg/L without additional electron donors to assess the degradability of the test chemical when present as the exogenous carbon source. Each bottle contained biomass expressed as organic carbon in the amount of 280 mg C/L for the glucose-fed culture and 230 mg C/L for the lactate-fed culture. The inoculums used in this study was two hexachlorobenzene (HCB) dechlorinating cultures were developed at 22°C us ing anaerobic media and contaminated estuarine sediment as inoculum . These mixed, methanogenic cultures were maintained in 9 L. (6L liquid volume) sealed glass reactors with a 14-day fill-and-draw cycle resulting in an average hydraulic retention time of 84 days. One culture was fed glucose (333 mg/L) while the other was fed lactate (333 mg/L) during each feeding cycle (7-9 days). Total gas production volume was determined by water displacement using a graduated buret and corrected for daily variations in atmospheric pressure. Methane was determined using an HP5890 Series II gas chromatograph (Hewlett Packard, Palo Alto, CA).
The percent degradation (% conversion) of test chemical was determined to be 42 % and 23 % by using Glucose fed culture and lactate feed culture as inoculums respectively by considering methane production as parameter at 22 oC temperature. On the basis of percent degradation value test chemical is considered to be biodegradable.
To further support the results of above mentioned study another study was reviewed from Journal Chemosphere (1994) in this study the Biodegradability of test chemical was determined by using different methods of OECD namely (DOC die away, Manometric respirometric and Closed bottle test) in 28 days. Initial test chemical concentration was 40 mg DOC/L, 100 mg/L and 2-10 mg/L respectively. The percent biodegradation of test chemical was determined to be 40, 45 and 18 % by different methods such as DOC die away , Mano- metric respirometric test and close bottle test. By considering percent degradation value it is concluded test chemical is inherently biodegradable in nature. Biodegradability of test chemical was determined by using different methods of OECD namely (DOC die away, Manometric respirometric and Closed bottle test) in 28 days. Initial test chemical concentration was 40 mg DOC/L, 100 mg/L and 2-10 mg/L respectively. The percent biodegradation of test chemical was determined to be 40, 45 and 18 % by different methods such as DOC die away , Mano- metric respirometric test and close bottle test. By considering percent degradation value it is concluded test chemical is inherently biodegradable in nature.
By considering the results of all the studies mentioned above it is concluded that test chemical is inherently biodegradable in nature.
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