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EC number: 229-880-6 | CAS number: 6805-41-0
- 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:
- 2016
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Version / remarks:
- 17 July 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Version / remarks:
- January 1998
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Escin
- EC Number:
- 229-880-6
- EC Name:
- Escin
- Cas Number:
- 6805-41-0
- Molecular formula:
- C110H172O48
- IUPAC Name:
- (2S,3S,4S,5R,6R)-6-{[(3S,4S,4aR,6aR,6bS,8R,8aR,9R,10R,12aS,14aR,14bR)-9-(acetyloxy)-8-hydroxy-4,8a-bis(hydroxymethyl)-4,6a,6b,11,11,14b-hexamethyl-10-[(2-methylbutanoyl)oxy]-1,2,3,4,4a,5,6,6a,6b,7,8,8a,9,10,11,12,12a,14,14a,14b-icosahydropicen-3-yl]oxy}-4-hydroxy-3,5-bis({[(2S,3R,4S,5S,6R)-3,4,5-trihydroxy-6-(hydroxymethyl)oxan-2-yl]oxy})oxane-2-carboxylic acid; (2S,3S,4S,5R,6R)-6-{[(3S,4S,4aR,6aR,6bS,8R,8aR,9R,10R,12aS,14aR,14bR)-9-(acetyloxy)-8-hydroxy-4,8a-bis(hydroxymethyl)-4,6a,6b,11,11,14b-hexamethyl-10-{[(2E)-2-methylbut-2-enoyl]oxy}-1,2,3,4,4a,5,6,6a,6b,7,8,8a,9,10,11,12,12a,14,14a,14b-icosahydropicen-3-yl]oxy}-4-hydroxy-3,5-bis({[(2S,3R,4S,5S,6R)-3,4,5-trihydroxy-6-(hydroxymethyl)oxan-2-yl]oxy})oxane-2-carboxylic acid
- Test material form:
- solid: bulk
Constituent 1
- Specific details on test material used for the study:
- Horse-Chestnut dry hydroalcoholic extract 16-22% contained saponin as escin according to Ph. Fr. X Ed.
Study design
- Oxygen conditions:
- not specified
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- Species: Activated sludge, microorganisms from domestic waste water treatment plant.
Preparation of Activated slugfe inoculum: The activated sludge used for this study was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was re-suspended in isotonic saline solution with shaking and again centrifuged. This procedure was repeated twice.An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to dry weight determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 5g dry material per litre was mixed with reconstituted water and then aerated under test condictions (for 6 days) until use. The pH of the activated sludge inoculum after preparation was: 7.34, just before use: 6.8. A pH adjustment of activated sludge inoculum was not performed.
Pre-conditioning of activated sludge inoculum: Pre-conditioning consisted of aerating (2L/minute) activate sludge (in mineral medium, reconstituted water) for 6 days at the test temperature. During the aeration the cell count of inoculum was checked as followS: the viability of the cultured sludge was determined by plating0.1 mL of the different, usually 10-2, 10-3, 10-4 and 10-5 dilutions of cultures on nutrient agar plates. The viable cell number of the cultures was determined by these plating experiments by manual colony counting. The approximately cell count of aerated inoculum fell in the range of 108 cells/L; thereforee on the day of the test this inoculum was diluted 1000x with reconstituted water to reach the necessary ca. 105 cells/L cell concentration. After preparation the sludge was filtered through cotton wool. Pre-conditioning improves the precision of the method. The inoculum was not pre-adapted to the test chemical. - Duration of test (contact time):
- 28 d
- Details on study design:
- Enviromental ondiction:
The test was carried out in a controlled enviroment room (during the formulation and oxygen measuring) at a temperature of 22+- 2°C according to the giudeline. The test flasks were incubated an a controlled environment room at 22+-2°C, in the dark. temperature was measured continously using min(max thermometer and noticed every day. During pre-conditioning of activated sludge inoculum the temperature was 20.1 - 21.7 °C; during the preparation, aeration and incubation of the reconstituted water preparation of the test bottles (units) the temperature was 20.3 - 21.3 °C. During the incubation (28 days) of the test units the temperature range was the following: 20.1 - 21.4°C. The oxygen concentration of the test water was in the range of 8-9 mg/L. It was measured at the start of the test and found to be 8.73 mf/L. The pH was checked prior study start and found to be 7.24. A pH adjustment was considered as not necessary. The test conditions were measured with suitable instruments and documented in the raw data.
Results and discussion
- Preliminary study:
- cfr attchment
- Test performance:
- cfr attchment
% Degradation
- Key result
- Parameter:
- % degradation (test mat. analysis)
- Value:
- >= 31 - <= 38.8
- Sampling time:
- 28 d
- Details on results:
- cfr attachment
BOD5 / COD results
BOD5 / COD
- Key result
- Parameter:
- COD
- Value:
- 60 mg O2/g test mat.
- Results with reference substance:
- CFR attachment
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The test item was considered to be not ready biodegradable. According to the test guidelines the pass level for biodegradability is 60% of COD.
In This study total oxydised nitrogen (nitrate and nitrite) concentration determination was not performed after each oxygen measurement.
According to the test guidelines the test item can be assumed as not inhibitory on the activated sludge microorganisms because the degradation in the toxicity control group was higher than 25% within 14 days.
The percentage biodegradation of the reference item confirms the suitability of the used activated sludge inoculum
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