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EC number: 629-661-9 | CAS number: 83834-59-7
- 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
Toxicity to aquatic plants other than algae
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic plants other than algae
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 221 (Lemna sp. Growth Inhibition Test)
- Version / remarks:
- 2006
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- - CAS no.: 83834-59-7
- Molecular formula: C18 H26 O3
- Molecular weight: 290.40 g/mole - Analytical monitoring:
- yes
- Details on sampling:
- - Analytical chemistry sample schedule: study day (SD) 0, 3, and 5 fresh (post-renewal) solution and SD 3, 5, and 7 (pre-renewal solution composite [waste])
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: recirculation through a saturator column
- Controls: negative (blank) control
- Evidence of undissolved material: no - Test organisms (species):
- Lemna minor
- Details on test organisms:
- TEST ORGANISM
- Common name: duck weed
- Clone: unknown
- Source: The L. minor culture originated from hydroponic cultures at Pond Megastore (Canton, OH USA) and has been cultured at the laboratory
- Age of inoculum: 3 weeks
- Method of cultivation: in SIS for 3 weeks
- Health status of test organisms: free from contamination of other organisms, healthy plant colonies (2-5 fronds) with high incidence of plants with >2 fronds, functioned as young rapidly growing plants without visible lesions or discoloration; no indications of algal contamination or infestation by other organisms
ACCLIMATION
- Acclimation period: 10 days
- Culturing media and conditions: same as test, sterile SIS medium
- Any deformed or abnormal plants observed: no - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 7 d
- Test temperature:
- 24º +/- 2 ºC (±2 ºC variation during in-life)
- pH:
- 6.5 - 9 (variability < 1.5)
- Dissolved oxygen:
- not specified
- Salinity:
- not applicable
- Conductivity:
- not specified
- Nominal and measured concentrations:
- Nominal: 0.0 (control), 0.0637 mg/L; measured:
- Details on test conditions:
- TEST SYSTEM
- Incubation chamber used: yes, temperature was maintained at 24 ± 2°C, with intra-replicate and treatment and inter-replicate and treatment variation not exceeding 2°C at any point during the in-life phase
- Test vessel: beakers
- Material, size: glass, 250 mL
- Aeration: no active aeration
- Agitation: no
- Renewal rate of test solution: renewal on study day 3 and 5
- No. of fronds per colony: 2 - 4
- Density on day 0: 10 fronds per replicate
- No. of vessels per concentration: 6
- No. of vessels per control: 6
GROWTH MEDIUM
- Standard medium used: yes, SIS (modified per OECD 221)
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: no
- Photoperiod: 16 h Light : 8 h dark
- Light intensity and quality: 6500 to 10000 lux (Measured at Water Surface)
EFFECT PARAMETERS MEASURED:
- Determination of frond number: manual counting
- Frond dry weight: On study day (SD) 0, the baseline frond dry weight was determined in six randomly selected samples containing 10 fronds each. On SD 7, all colonies were collected from each of the test vessels and rinsed with deionized water. The colonies were then blotted to remove excess water and then dried at 60°C overnight. The dry weight was expressed to an accuracy of 0.1 mg.
- Determination of frond area: Computer-aided digitization of digital photographs (Sigma Scan Pro, SPSS, Chicago, IL USA)
- Other: Changes in plant development, including frond size, appearance, indication of necrosis, chlorosis or gibbosity, colony break-up or loss of buoyancy, and in root length and appearance, were monitored during the in-life phase. Significant features of the test medium (e.g. presence of undissolved material, growth of algae in the test vessel) were also monitored.
RANGE-FINDING STUDY
- Test concentrations: ca. 0.050 mg/L, 0.013, 0.0032 and 0.0 (contrl) mg/L
- Results used to determine the conditions for the definitive study: yes, based on the range-finding, a limit test based on an estimated practical water solubility of 0.05 mg/L OMC was designed for definitive study.- Reference substance (positive control):
- no
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- dry weight
- yield
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- dry weight
- yield
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- dry weight
- growth rate
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- dry weight
- growth rate
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- frond area
- growth rate
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- frond area
- yield
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- frond area
- growth rate
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.06 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- frond area
- yield
- Remarks on result:
- other: no effect detected up to and including the water solubility limit of the substance
- Details on results:
- I. Fronds
- Frond number: The mean frond number at study day (SD) 7 in the control (0.0 mg/L) and 0.05 mg/L OMC treatment were 130 ± 2 (SEM) and 130 ±2 (SEM), respectively. The mean total frond count at SD 7 in the 0.05 mg/L OMC treatment was not significantly different from the control (t-test, p = 0.846).
- Doubling Time : The mean and median doubling time in the control (0.0 mg/L) and 0.05 mg/L OMC treatment were both 1.90±0.01 (SEM) days, respectively. The doubling time through SD 7 in the 0.05 mg/L OMC treatment was not significantly different from the control (Mann-Whitney Rank Sum test, p=1.000).
- Total Frond Area: Mean total frond area were 871 ± 18 (SEM) and 916 ± 18 (SEM) mm2 in the control (0.0 mg/L) and 0.05 mg/L OMC treatment on SD 7, respectively. Frond area measured in the 0.05 mg/L OMC on SD 7 was not significantly different than the control (t-test, p = 0.105).
- Frond Weight: Mean frond dry weight were 0.0220± 0.0019 and 0.0203 ±0.0029 g in the 0.00 mg/L (control) and the 0.05 mg/L OMC treatment on SD 7, respectively. Mean frond dry weight measured in the 0.05 mg/L OMC treatment on SD 7 was not significantly different than the control (t-test, p = 0.646).
II. Clinical Signs of Toxicity: Clinical signs of toxicity were not observed during the conduct of the present study.
III. Average Specific Growth Rates
- Frond Area: The average specific growth rate based on frond area for the control (0.0 mg/L) and 0.05 mg/L OMC treatment were 0.3 ± 0.0 and 0.3±0.0, respectively. The CVs for the average specific growth rate based on frond area for the control (0.0 mg/L) and 0.05 mg/L OMC treatment were 0.0 % and 0.0 %, respectively. The mean average specific growth rate based on frond area for the 0.05 mg/L OMC treatment was not significant different from the control (Mann-Whitney Rank Sum test, p = 1.000). The percent inhibition in growth (Ir) was 0.0 %.
- Frond Dry Weight: The average specific growth rate based on frond dry weight for the control (0.0 mg/L) and 0.05 mg/L OMC treatment were 0.3320 ± 0.0129 and 0.3160 ± 0.0223, respectively. The CVs for the average specific growth rate based on frond dry weight for the control (0.0 mg/L) and 0.05 mg/L OMC treatment were 9.4900 % and 17.2989 %, respectively. The mean average specific growth rate based on frond dry weight for the 0.05 mg/L OMC treatment was not significant different from the control (t-test, p = 0.543). The percent inhibition in growth (Ir) was 4.9 %. However, since the study design was based on a limit test and no significant difference in average specific growth weight based on dry weight was found between the 0.05 mg/L OMC treatment and the control (0.0 mg/L), the minimal percent inhibition calculated was deemed insignificant and inconsequential to the interpretation of the study results.
IV. Yield
- Frond Area: The normalized biomass (bc) for the control and 0.05 mg/L OMC treatment were 785 and 814 mm^2, respectively. The mean yield based on frond area for the 0.05 mg/L OMC treatment was not significant different from the control (t-test, p = 0.279). The percent reduction in yield was -4% (calculated value, or theoretically 0.0).
- Frond Dry Weight: The normalized biomass (bc) for the control and 0.05 mg/L OMC treatment were 0.0198 and 0.0182 g, respectively. The mean yield based on frond dry weight for the 0.05 mg/L OMC treatment was not significant different from the control (t-test, p =0.646). The reduction in yield was 8.1%. However, since the study design was based on a limit test and no significant difference in average specific growth weight based on dry weight was found between the 0.05 mg/L OMC treatment and the control (0.0 mg/L), the minimal percent inhibition calculated was deemed insignificant and inconsequential to the interpretation of the study results.
- Any visual signs of phytotoxicity (abnormalities): no
- Decrease in frond size: no
- Necrosis / chlorosis: no
- Sinking of fronds: no
- Sterility: no
- Any stimulation of growth found in any treatment: no
- Any observations that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: no- Results with reference substance (positive control):
- positive control not performed
- Reported statistics and error estimates:
- Formal statistical analysis was based on hypothesis tests comparing the average specific growth rate and yield (biomass) in the control to the OMC treatment. The data were evaluated for normality (Shapiro-Wilk’s test) and homogeneity (Levene’s test). For non-normally distributed data or data with a heterogeneous distribution of variance; the Mann-Whitney Rank Sum test was used. For normally distributed data sets with homogeneous variance, a Student’s t-test was used to evaluate the data. The statistical significance of all tests indicated was assessed at p = 0.05 and the replicate was considered the experimental unit.
Table 1: Summary of Results
Endpoints
0.0 OMC
(mg/L)
0.06 OMC
(mg/L)
Day 7
Fronds (no.)
---
NS
Doubling Time (days)
---
NS
Frond Area (mm)
---
NS
Frond Weight (g)
---
NS
ASGR (area)
---
NS
ASGR (weight)
---
NS
Yield (bt[1], area)
---
NS
Yield (bt1, weight)
---
NS
Growth Inhibition (%, area)
---
6.1
Growth Inhibition (%, weight)
---
4.9
Yield Inhibition (%, area)
---
0.0
Yield Inhibition (%, weight)
---
8.1
Clinical
NF
NF
NS – not signficant compared to the control.
NF – No clinical findings.
[1] Treatment biomass.
Table 1: Summary of Performance Criteria
Criterion
Acceptable Limits
Criteria Passed
Control doubling time
The doubling time of frond number in the control must be less than 2.5 days (60 hours), corresponding to approximately a seven-fold increase in seven days.
Yes
Control average specific growth rate
An average specific growth rate of 0.275/d.
Yes
pH
Not increase by more than 1.5 s.u.
Yes
Light Intensity
6500-10000 not exceeding ±15% within test area.
Yes
Water temperature
24 ± 2°C with inter-replicate variability ≤ 2°C
Yes
Table 3: Summary of OMC Concentrations in the Lemna minor Growth Inhibition Test
Study Day
Treatment Target Concentration (mg/L)
Replicate
Sample ID[1]
Measured Concentration (mg/L)[2]
24-h Stability (%)
0
0.00
Fresh
009
<LOD
---
0.050
Fresh
010
0.0574
---
3
0.00
Fresh
016
<LOD
---
A (Waste)
012
<LOD
100.0
B-G (Waste)
013
<LOD
100.0
0.050
Fresh
017
0.0548
---
A (Waste)
014
0.0547
99.8
B-G (Waste)
015
0.0550
100.4
5
0.00
Fresh
023
<LOD
---
A (Waste)
019
<LOD
100.0
B-G (Waste)
020
<LOD
100.0
0.050
Fresh
024
0.0630
---
A (Waste)
021
0.0598
94.9
B-G (Waste)
022
0.0600
95.2
7
0.00
Fresh
030
<LOD3
---
A (Waste)
026
<LOD
100.0
B-G (Waste)
027
<LOD
100.0
0.050
Fresh
031
0.0687[3]
---
A (Waste)
028
0.0659
95.9
B-G (Waste)
029
0.0648
94.3
[1] Pre-renewal (waste) samples were collected from replicate A and a composite of replicates B-G of the control and the OMC treatment.
[2] Limit of Detection (LOD) = 0.000972 mg/L.
[3] Tested for verification, but not used in in-life phase.
Table 5: Mean Measured and Time-Weight Mean OMC Concentrations in the Lemna minor Growth Inhibition Test
Treatment Target Concentration (mg/L)
Replicate
Mean Measured Concentration (mg/L)[1]
Time-Weighted Mean (mg/L)[2]
Intra-Replicate CV[3] (%)
24-h Stability[4] (%)
0.00
Fresh
<LOD[5]
<LOD
0.0
---
A (Waste)
<LOD
<LOD
0.0
100.0
B-G (Waste)
<LOD
<LOD
0.0
100.0
0.050
Fresh
0.0584
---
10.1
---
A (Waste)
0.0601
0.0579
9.3
105.5
B-G (Waste)
0.0599
0.0578
8.2
105.1
[1] The fresh solution mean measured concentration represent the arithmetic mean of each data point from SD 0, 3, and 5. The pre-renewal (waste) mean measured concentration represents the arithmetic mean of each data point from SD 3, 5, and 7 for replicate A and composite of replicates B-G of the control and OMC treatment.
[2] Determined in accordance with OECD 211, Annex 6.
[3] Coefficient of variation = (Standard deviation / mean)*100.
[4] Stability = (Mean Measured Waste / Mean Measured Fresh)*100.
[5] Limit of Detection (LOD) = 0.000972 mg/L.
Table 6: Effect of OMC Exposure on Lemna minor Frond Number – SD 7
Treatment Target Concentration [Time Weighted Mean] (mg/L)
ID
Count
Frond Number
N (Replicates)
Mean
Median
Standard Deviation
Standard Error
0.00
[<LOD]
B
1
130
6
130
129
4
2
C
1
134
D
1
128
E
1
135
F
1
126
G
1
124
0.050
[0.0578][1]
B
1
132
6
130
130
4
2
C
1
126
D
1
128
E
1
136
F
1
125
G
1
133
[1] Not significantly different from control (t-test, p=0.846).
Table 7: Effect of OMC Exposure on Lemna minor Average Specific Growth Rate (Weight) – SD 7
Treatment Target Concentration [Time Weighted Mean] (mg/L)
ID
Count
ASGR[1]
N (Replicates)
Mean
Median
Standard Deviation
Standard Error
0.00
[<LOD]
B
130
0.3527
6
0.3320
0.3420
0.0316
0.0129
C
134
0.3045
D
128
0.3438
E
135
0.3685
F
126
0.3407
G
124
0.2846
0.050
[0.0578][2]
B
132
0.3527
6
0.3160
0.3360
0.0547
0.0223
C
126
0.2604
D
128
0.3556
E
136
0.3711
F
125
0.3184
G
133
0.2391
[1] ASGR = Average Specific Growth Rate
[2] Not significantly different from control (t-test, p=0.543).
- Validity criteria fulfilled:
- yes
- Conclusions:
- Results from the present study indicated that L. minor growth was not significantly inhibited by exposure to the practical soluble level of OMC (0.06 mg/L OMC, measured time weighted average) in the present study. Therefore, the 7-day EC50 and 7-day NOEC based on growth and yield, respectively is considered to be 0.06 mg/L OMC (measured time weighted average).
- Executive summary:
To assess the potential adverse effect of the test item on growth of Lemna minor in hydroponic culture, a Lemna sp. Growth Inhibition Test according to OECD TG 221 was carried out. Actively growing L. minor cultures were inoculated as monocultures in one test item concentration of 0.0637 mg/L representing the limit of practical solubility in SIS media over a period of seven days (limit test). For this assay 6 replicates with 10 fronds per replicate were prepared using a saturator column. The nominal test concentration was measured using LC-MS/MS to be 0.0578 mg/L OMC (time weighted mean). The stability over the course of the in-life phase ranged from 105.5 % to 105.1 % and the CVs of the intra-replicate was 12.1 %for the fresh solution and ranged between 9.3 and 8.2 % for the old media, which is in line with the criteria given in the guideline. Frond number was the primary measurement endpoint, whereas total frond area and dry weight were also measured. A semi-static study design with renewal on days 3 and 5 was used. Control doubling time was <2.5 days. The range of pH measured in the control and treatments was between 6.5 and 9 and ≤1.5 throughout this study, the temperature in the study was maintained at 20±2ºC, and the inter-replicate range in temperature was maintained at ≤2 ºC. In summary, the present study met all performance criteria established for the OECD Test Guideline 221. As a result, the mean frond number at SD 7 in the control (0.0 mg/L) and 0.05 mg/L OMC treatment were both 130±2 (SEM). The total frond count at SD 7 in the 0.05 mg/L OMC treatment was not significantly different from the control (t-test, p=0.846). The mean average specific growth rate based on frond area for the 0.05 mg/L OMC treatment was not significantly different from the control (Mann-Whitney Rank Sum test, p=1.000). The percent inhibition in growth (Ir) was 0.0%. Clinical signs of toxicity were not observed during the conduct of the present study. In conclusion, results from the present study indicated that L. minor growth was not significantly inhibited by exposure to the practical soluble level of OMC (0.06 mg/L OMC) in the present study. The 7-day EC50 and NOEC for growth rate and yield were both determined to be > 0.06 and >= 0.06 mg/L (measured, TWA), respectively, i.e. higher than the water solubility level of the substance.
Reference
Description of key information
Results from the study indicated that L. minor growth was not significantly inhibited by exposure to the practical soluble level of OMC (0.06 mg/L OMC, measured time weighted average). Therefore, the 7-day EC50 and 7-day NOEC based on growth and yield, respectively is considered to be > 0.06 mg/L and >= 0.06 mg/L (measured time weighted average), respectively.
Key value for chemical safety assessment
Additional information
To assess the potential adverse effect of the test item on growth of Lemna minor in hydroponic culture, a Lemna sp. Growth Inhibition Test according to OECD TG 221 was carried out. Actively growing L. minor cultures were inoculated as monocultures in one test item concentration of 0.0637 mg/L representing the limit of practical solubility in SIS media over a period of seven days (limit test). For this assay 6 replicates with 10 fronds per replicate were prepared using a saturator column. The nominal test concentration was measured using LC-MS/MS to be 0.0578 mg/L OMC (time weighted mean). The stability over the course of the in-life phase ranged from 105.5 % to 105.1 % and the CVs of the intra-replicate was 12.1 % for the fresh solution and ranged between 9.3 and 8.2 % for the old media, which is in line with the criteria given in the guideline. Frond number was the primary measurement endpoint, whereas total frond area and dry weight were also measured. A semi-static study design with renewal on days 3 and 5 was used. Control doubling time was <2.5 days. The range of pH measured in the control and treatments was between 6.5 and 9 and ≤1.5 throughout this study, the temperature in the study was maintained at 20 ± 2 ºC, and the inter-replicate range in temperature was maintained at ≤2 ºC. In summary, the present study met all performance criteria established for the OECD Test Guideline 221. As a result, the mean frond number at SD 7 in the control (0.0 mg/L) and 0.05 mg/L OMC treatment were both 130±2 (SEM). The total frond count at SD 7 in the 0.05 mg/L OMC treatment was not significantly different from the control (t-test, p=0.846). The mean average specific growth rate based on frond area for the 0.05 mg/L OMC treatment was not significantly different from the control (Mann-Whitney Rank Sum test, p=1.000). The percent inhibition in growth (Ir) was 0.0%. Clinical signs of toxicity were not observed during the conduct of the present study. In conclusion, results from the present study indicated that L. minor growth was not significantly inhibited by exposure to the practical soluble level of OMC (0.06 mg/L OMC) in the present study. The 7-day EC50 and NOEC for growth rate and yield were both determined to be > 0.06 and >= 0.06 mg/L (measured, TWA), respectively, i.e. higher than the water solubility level of the substance.
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