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EC number: 214-244-2 | CAS number: 1117-31-3
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vitro / ex vivo
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 27 Jul - 29 Aug 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP-Guideline study with acceptable restrictions. No hydrolysis test in saliva and gastric juice simulants.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
- Objective of study:
- other: hydrolysis in intestinal fluid simulant
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: European Food Standard Authority, Food Contact Materials, Note for Guidance (updated 30/07/2008), Annex 1 to Chapter III
- Deviations:
- yes
- Remarks:
- no hydrolysis test in saliva and gastric juice simulants
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the Government of the United Kingdom
Test material
- Reference substance name:
- Ethylene di(acetate)
- EC Number:
- 203-881-1
- EC Name:
- Ethylene di(acetate)
- Cas Number:
- 111-55-7
- Molecular formula:
- C6H10O4
- IUPAC Name:
- ethane-1,2-diyl diacetate
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- other: not specified; presumably pig in accordance with the test method used
- Strain:
- not specified
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- TEST DIGESTIVE SIMULANTS
INTESTINAL FLUID SIMULANT
- Description: Intestinal fluid simulant in accordance with the guideline
- Preparation: Potassium dihydrogen orthophosphate (KH2PO4) (3.41 g) was dissolved in approximately 125 mL of reverse osmosis (RO) water, in a 500 mL volumetric flask. Approximately 95 mL of 0.2 M sodium hydroxide (NaOH) was added followed by a further 200 mL of RO water. Pancreatic extract (5.00 g) was weighed into a 150 mL beaker and approximately 75 mL of RO water added gradually with stirring. The solution was then transferred to the volumetric flask containing the basified KH2PO4. Sodium taurocholate (0.25 g) was added and the mixture shaken gently. The pH of the solution was adjusted to pH 7.5 ± 0.1 using 0.2 M NaOH. The solution was diluted to volume using RO water and shaken thoroughly to mix.
Administration / exposure
- Route of administration:
- other: mixing
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- - Preparation of the Test Solutions
Sample solutions were prepared in capped glass vessels at a nominal concentration of 1.5 g/L (equivalent to approximately 0.01 mol/L) in the intestinal fluid simulant.
The test solutions were split into individual vessels for each data point.
The solutions were shielded from light whilst maintained at the test temperature.
- Testing
The sample solutions were maintained at 37.0 ± 0.5 °C for a period of 1, 2 and 4 h. - Duration and frequency of treatment / exposure:
- 1, 2 and 4 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1.5 g/L (equivalent to approximately 0.01 mol/L)
- No. of animals per sex per dose / concentration:
- triplicate determinations
- Control animals:
- other: for GC: blank samples from intestinal fluid simulant and samples of reference materials (parent substance and hydrolysis products), all diluted 1:10 in acetone
- Details on study design:
- - Principle of the Test
The test item was dissolved in the requisite test medium and the solution incubated in the dark and at 37.0 ± 0.5 °C in a water bath. The concentration of the test item was determined as a function of time, using a suitable analytical method. For decreasing concentrations, the logarithms of the concentrations were plotted against time (log10 (Ct)). For plots resulting in a straight line, the reaction is considered to be of (pseudo-) first order. The rate constant and the half-time are then calculated using the slope. - Details on dosing and sampling:
- - Analysis of the Sample Solutions
Triplicate sample solutions were taken from the water bath after the specified incubation period and the pH of each solution recorded. The concentration of the sample solution was determined by gas chromatography (GC).
- Controls
Standards: Duplicate standard solutions of a mixture of test item, acetic acid and ethanediol were prepared in acetone at nominal concentration of 150 mg/L each.
Samples: An aliquot of each sample solution was diluted by a factor of 10 using acetone.
Matrix blanks: Intestinal fluid simulant diluted by a factor of 10 using acetone.
- Analysis
The standard and sample solutions were analysed by GC using the following conditions:
GC system: Agilent Technologies 6890, incorporating workstation
Column: DB-624 (60 m x 0.25 mm id x 1.4 µm film)
Oven temperature program: initial 40 °C for 2 min; rate 10 °C/min; final 80 °C for 0 min; rate 20 °C 7min; final 240 °C for 8 min
Injection mode: splitless (purge on at 0.5 min)
Flow rate: 0.75 mL/min
Injection temperature 300 °C
FID detector temperature: 250 °C
Injection volume: 1 µL
Retention time: Acetic acid ca. 9.7 min; Ethanediol ca. 11.4 min; Test item ca. 14.1 min
- Data handling
Sample solution concentration: The response factors of the standard peak areas (unit peak area per mg/L) were calculated using Equation 1:
RF = (Rstd/Cstd) [Equation 1]
Where:
RF = response factor for the standard solution
Rstd = peak area for the standard solution
Cstd = concentration for the standard solution (mg/L)
The sample solution concentration (g/L) was calculated using Equation 2
C = (Rspl/RFstd) x (D/1000) [Equation 2]
Where:
C = sample solution concentration (g/L)
Rspl = mean peak area for the sample solution
RFstd = mean response factor for the standard solutions (unit peak area per mg/L)
D = dilution factor (10)
- Degree of Hydrolysis
The decrease in concentration of test item or the degree of hydrolysis was calculated using Equation 3.
Degree of hydrolysis in percent = ((C0 – Ct)/C0) x 100 [Equation 3]
Where:
C0 = concentration at time 0
Ct = concentration at time t
- Half-life
For confirmation of first order kinetics, the data obtained in the tests were plotted as log10 (Ct) versus t.
From this plot the reaction rate constant (Kobs) was obtained from the slope, where the slope of the resultant line was calculated using linear regression analysis as per Equation 4.
Kobs = -2.303 x slope [Equation 4]
The half-life time of the reaction was calculated using Equation 5.
t1/2 = 0.693/Kobs [Equation 5] - Statistics:
- Mean values of triplicate determinations were calculated.
Results and discussion
Main ADME results
- Type:
- other: degree of hydrolysis
- Results:
- 4.37, 6.42 and 10.5% after 1, 2 and 4 h, respectively
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Not applicable
- Details on distribution in tissues:
- Not applicable
- Details on excretion:
- Not applicable
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: 25.9 h at 37 °C
- Test no.:
- #1
- Toxicokinetic parameters:
- other: rate constant = 7.42E-06 per sec
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Acetic acid concentration was determined in the initial (0 h) and in the 1, 2, and 4 h samples.
The corresponding mean concentrations were 74.9, 220, 261 and 423 mg/L at 0, 1, 2 and 4 h, respectively.
Ethanediol concentrations were not determined.
A peak in the chromatography at approximately 12.7 minutes, which was not present in the standard solutions, was observed to increase in magnitude over the period of the test. This was not identified or quantified but was considered most likely to be ethylene glycol monoacetate, a degradation product of the test item.
Any other information on results incl. tables
Table 1. Degree of hydrolysis
Sample |
Sample pH (mean of 3 samples) |
Mean concentration (mg/L), n=3 |
Log10 Concentration (mg/L) |
Degree of hydrolysis (%) |
Initial |
7.45 |
1503 |
3.177 |
- |
1 h |
7.36 |
1438 |
3.158 |
4.37 |
2 h |
7.35 |
1407 |
3.148 |
6.42 |
4 h |
7.27 |
1345 |
3.129 |
10.5 |
Table 2. Results of linear regression
Slope |
-1.16E-02 |
Kobs |
2.67E-02 per h (7.42E-06 per sec) |
t1/2 |
25.9 h (1.08 days) |
Table 3. Acetic acid concentration
Sample |
Mean concentration (mg/L), n=3 |
Initial |
74.9 |
1 h |
220 |
2 h |
261 |
4 h |
423 |
Validation
The linearity of the detector response with respect to concentration was assessed over the concentration range of 15 to 300 mg/L for both test item an acetic acid. This was satisfactory with correlation coefficients (r) of 0.999 being obtained for each analyte.
Discussion
It was observed that the concentration of acetic acid in the sample solutions increased with time and was most likely due to hydrolysis of the test item.
A peak in the chromatography at approximately 12.7 minutes, which was not present in the standard solutions, was observed to increase in magnitude over the period of the test. This was not identified or quantified but was considered most likely to be ethylene glycol monoacetate, a degradation product of the test item.
Conclusion
The rate constant and half-life at 37 °C of the test item in simulated intestinal fluid at pH 7.5 were determined and are shown below.
Table 4. Rate constant and half-life time
Rate constant (per sec) |
Estimated half-life at 37 °C |
7.42E-06 |
25.9 h |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): bioaccumulation potential cannot be judged based on study results
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