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EC number: 202-653-9 | CAS number: 98-29-3
- 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
Toxicity to microorganisms
Administrative data
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 7 sept 2009 to 23 nov 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 4-tert-butylpyrocatechol
- EC Number:
- 202-653-9
- EC Name:
- 4-tert-butylpyrocatechol
- Cas Number:
- 98-29-3
- Molecular formula:
- C10H14O2
- IUPAC Name:
- 4-tert-butylbenzene-1,2-diol
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Based on the information provided by the Sponsor, the test item is soluble at a concentration of about 2 g/L in water. Based on the results of a pre-test (without GLP), the test item was not soluble at a concentration of 1 g/L in tap water under the pre-test conditions.
Therefore, test item amounts of 5.05, 16.08, 50.22, 160.42 and 500.42 mg were weighed by means of an analytical balance and transferred to the designated test vessels with 284 mL tap water. The test item was mixed into the tap water by intense stirring for 30 minutes at room temperature to dissolve a maximum amount of the test item and/or disperse it as homogeneously as possible. No emulsifiers or solvents were used.
After a stirring period of 30 minutes, the appearance of the test media was evaluated, and in all test concentrations (except for the lowest test concentration of 10 mg/L) the test item
4-Tert-Butylpyrocatechol (4-TBC) was not completely dissolved in the test media under the test conditions. Then, 16 mL synthetic sewage feed and 200 mL activated sludge inoculum were added.
- Controls: two controls containing only tap water, synthetic sewage feed and inoculum were tested in parallel to the five concentrations of the test item under identical test conditions.
Test organisms
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- - Laboratory culture: no, aerobic activated sludge came from a wastewater treatment plant (ARA Ergolz II, Füllinsdorf / Switzerland).
- Method of cultivation: During the holding period of three days prior to use, the sludge was fed daily with 50 mL synthetic sewage feed per liter and was kept at room temperature under continuous aeration until use. The pH of the activated sludge inoculum was 7.7.
- Preparation of inoculum for exposure: The sludge was washed twice with tap water by centrifugation and the supernatant liquid phase was decanted. An aliquot of washed sludge was suspended in tap water to obtain a concentration equivalent to 3 g dry material per liter.
- Pretreatment: no
- Initial biomass concentration: 3 g dry material per liter
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Post exposure observation period:
- none
Test conditions
- Hardness:
- no data
- Test temperature:
- The temperature in the test media, measured in one control, was 20°C at the start and at the end of the incubation period
- pH:
- At the beginning and at the end of the 3-hour incubation, the pH value was in the range of 7.6 to 8.4.
- Dissolved oxygen:
- At the beginning and at the end of the 3-hour incubation, the oxygen concentration value was in the range of 8.0 to 8.9 mg O2/L.
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- nominal concentrations: 10, 32, 100, 320 and 1000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type: open
- Material, size, headspace, fill volume: The test was performed in 2000 mL glass beakers.
- Aeration: During the incubation period of 3 hours all test media and the controls were continuously aerated by intense stirring on magnetic stirrers to avoid possible foaming and/or stripping of the test item.
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 2
- Biomass loading rate: sludge concentration = 1.6 g dry material / L
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: tap water
- Total organic carbon, Particulate matter, Metals, Pesticides, Chlorine, Alkalinity, Ca/mg ratio, Conductivity: no data
- Culture medium different from test medium: no
- Intervals of water quality measurement: The pH values and dissolved oxygen concentrations were determined after the addition of synthetic sewage feed and activated sludge in all test media and the controls at the start and at the end of the 3-hour incubation period. The water temperature was measured in one control at the start and at the end of the incubation period. Before the addition of activated sludge and synthetic sewage feed, the appearance of the test media was recorded.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: no data
- Light intensity: no data
EFFECT PARAMETERS MEASURED: For measurement of the respiration rate a well-mixed sample of each test medium was poured into a BOD-flask after three hours incubation time, and was not further aerated. Then the dissolved oxygen concentration was measured with an oxygen electrode (WTW TriOxmatic® 300 and an oxygen meter WTW Oxi 539, Wissenschaftlich-Technische Werkstaetten WTW, Weilheim/Germany), and was continuously recorded. During measurement, the samples were continuously stirred on a magnetic stirrer. The oxygen consumption rate (in mg O2 L-1 minute-1) was determined from the linear part of the respiration curve in the range 6.5–2.5 mg O2/L. In case of very rapid oxygen consumption, the range used was below the limits indicated above but always within the linear part of the respiration curve. In case of low oxygen consumption the rate was determined over a period of at least ten minutes.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.1 / 3.2
- Range finding study: none
- Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol tested at 5, 16 and 50 mg/L
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: 0.0 - 3.0 mg/L
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- 16 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: 3.5 - 32 mg/L
- Details on results:
- At the lowest test concentration of 10 mg/L, the test item 4-Tert-Butylpyrocatechol (4-TBC) had a significant inhibitory effect of 41% on the respiration rate of activated sludge after the incubation period of three hours. At the next higher test item concentration of 32 mg/L, the inhibitory effect increased to 61%. At the following test item concentrations of 100, 320 and 1000 mg/L, a plateau was reached with inhibitory effects of 82, 89 and 87%, respectively.
The oxygen consumption rates of the two controls (run at the start and at the end of the test) differed by 9% (guideline-recommendation: the two control respiration rates should be within 15% of each other). - Results with reference substance (positive control):
- The 3-hour EC50 of the reference item 3,5-dichlorophenol (positive control) was calculated to be 11 mg/L with 95% confidence limits from 0.9 to 55 mg/L. The 3-hour EC50 is within the guideline-recommended range of 5–30 mg/L, confirming suitability of the activated sludge used.
Any other information on results incl. tables
Table 1: Influence of 4-tert-butylpyrocatechol (4 -TBC) and 3,5-dichlorophenol on the oxygen consumption of activated sludge
Nominal concentration of test chemical |
Oxygen consumption rate |
Inhibition |
(mg/L) |
(mg O2L-1min-1) |
(%) |
Control |
|
|
0 |
0.891 |
|
0 |
0.972 |
|
Mean |
0.932 |
|
Deviation (%) |
9.0 |
|
Test item: 4-TBC |
|
|
10 |
0.552 |
40.7 |
32 |
0.366 |
60.7 |
100 |
0.172 |
81.5 |
320 |
0.106 |
88.6 |
1000 |
0.126 |
86.5 |
Reference item: 3,5-dichlorophenol |
|
|
5 |
0.718 |
22.9 |
16 |
0.313 |
66.4 |
50 |
0.084 |
91.0 |
% inhibition: increased oxygen consumption rate relative to control
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- The EC50 of the reference item is in the acceptance range and the oxygen consumption rates of the 2 controls differed by less than 15%.
- Conclusions:
- The concentration of the test item 4-tert-butylpyrocatechol (4-TBC) leading to an inhibitory effect of 50% on the respiration rate of activated sludge after the incubation period of three hours, compared with the mean respiration rate of two controls, is calculated to be 16 mg/L (with 95% confidence limits of 3.5 – 32 mg/L).
- Executive summary:
In a study (Harlan, 2009), the inhibitory effect of the substance 4-tert-butylpyrocatechol on the respiration rate of aerobic wastewater microorganisms of activated sludge was investigated in a 3-hour respiration inhibition test according to OECD guideline for Testing of Chemicals, n°209 (1984).
The nominal concentrations tested were 10, 32, 100, 320 and 1000 mg/L.
In addition, two controls and three different concentrations of the reference item 3,5-dichlorophenol (5, 16 and 50 mg/L) were tested in parallel. The results of these reference treatments (EC50 = 11 mg/L within the guideline-recommended range of 5 - 30 mg/L) confirmed suitability of the activated sludge.
EC50 = 16 mg/L (95% C.L.: 3.5 - 32 mg/L)
NOEC = 0.6 mg/L (95% C.L.: 0.0 - 3.0 mg/L)
Based on the results of this study, 4 -tert-butylpyrocatechol would be considered as harmful for microorganisms.
This study is classified as acceptable and satisfies the guideline requirements for toxicity study to activated sludge in a respiration inhibition test.
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