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EC number: 204-881-4 | CAS number: 128-37-0
- 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
Toxicity to soil microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil microorganisms
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Endpoint:
- toxicity to soil microorganisms
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Reason / purpose for cross-reference:
- reference to same study
- Principles of method if other than guideline:
- The inhibition of cell duplication of Bacillus subtilis was measured at different doses for several compounds including BHT. The increase in the cell number per mL was measured by the increase in the optical density at 600 nm.
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Details on preparation and application of test substrate:
- VEHICLE:
- Chemical name of vehicle: The publications includes studies on several substances among which was BHT. The solvent used for BHT is not specified. However, the solvents used to dissolve the compounds were either ethanol (95%) (the final concen- tration was not more than 1%); dimethylsulfoxide (Sigma Chem. Co.) (the final concentration was not more than 1%); sodium hydroxide (the final concentration was not more than 9 mM); or distilled water. - Test organisms (inoculum):
- other: Bacillus subtilis (60015 trpC metC)
- Total exposure duration:
- 60 min
- Test temperature:
- 37ºC
- Details on test conditions:
- TEST SYST
- Test container (type, material, size): When the bacterial culture reached an OD600 of 0.35, 1-mL samples were placed into Prewarmed small plastic tubes (automated method) or 125 mL Erlenmeyer flasks (Flask method)
- Test conditions:
In the automated method, four controls were run, two with added solvent and two with added distilled water. The tubes were located in an aluminum block and aerated at 37°C through stainless steel tubes. Sixty minutes later the OD600 of the cultures in the tubes were read automatically in a Gilford spectrometer 300N and the results fed into a computer, which calculated the inhibition index.
With the flask method a 1-mL sample was withdrawn every 15 or 20 minutes, the OD600 was read in a Gilford spectrometer 240GH and the inhibition index was determined at 60 minutes after the addition of the inhibitor.
EFFECT PARAMETERS MEASURED
Concentration in mM required for 50 % inhibition in rate of duplication (IC50).
VEHICLE CONTROL PERFORMED: yes
- Nominal and measured concentrations:
- Unspecified. Different amounts of inhibitor (BHT).
- Reference substance (positive control):
- not specified
- Duration:
- 60 min
- Dose descriptor:
- EC50
- Remarks:
- Based on growth inhibtion
- Effect conc.:
- 0.1 other: mM
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Growth inhibition.
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The concentration of BHT required to inhibit 50 % the growth of Bacillus subtilis was 0.1 mM equivalent to 22.04 mg/L
- Executive summary:
A inhibition growth test in Bacillus subtilis was performed with BHT among other substances. The growth of the bacteria was evaluated by optical absorbance at 600 nm. Two methos were used; an automated method and a flask method. When bacterial cultures reached and OD600 of 0.35 different amounts of sample were placed in plastic tubes (automated method) or Erlen meyer flasks which already contained different amounts of BHT. In all samples the amount of solvent used to dissolve the inhibitor was the same. In the automated method, four controls were run, two with added solvent and two with added distilled water. The tubes were located in an aluminum block and aerated at 37°C through stainless steel tubes. Sixty minutes later the OD600 of the cultures in the tubes were read automatically in spectrometer and the results fed into computer which calculated the inhibition index. With the flask method a 1-ml sample was withdrawn every 15 or 20 minutes, the OD600 was read in a spectrometer and the inhibition index was determined at 60 minutes after the addition of the inhibitor. The concentration of BHT required to inhibit 50 % the growth of Bacillus subtilis was 0.1 mM, equivalent to 22.04 mg/L.
Referenceopen allclose all
The inhibition of cell duplication of Bacillus subtilis was measured at different doses for several compounds including BHT. The increase in the cell number per ml was measured by the increase in the optical density at 600 nm. The cell number was determined at different times in different culture dishes (all plated at the same time) using a Cytograph. The inhibition was quantitated by an inhibition index defined as :
I = 1- (B2-Bl)/(A2-A1)
where
B is the culture value (OD600 or cell number per plate) in the presence of the inhibitor and A the culture value in the absence of the inhibitor. These culture values were determined at different times after the cells had been exposed to the inhibitor. For B. subtilis, A1 and B1 were measured immediately after addition of the compound, A2 and B2 60 minutes later.
One can characterize the potency by interpolating between the observed values and determining the concentration needed to produce a certain extent of inhibition; in this paper the concentration that produces 50% inhibition of growth was used.
Description of key information
Toxicity of BHT to microorganisms was studied using the test organisms: P. fluorescens, Tetrahymena pyriformis and Photobacterium phosphoreum (Vibrio fischeri).
The 30min-EC50 of BHT to Photobacterium phosphoreum based on light emission is 8.98 mg/L.
In a growth inhibition test with P. fluorescens, the EC50 was greater than the highest tested concentration of 50 mg/L (Trevors et al., 1981).
A 24-h EC50 of 1.7 mg/l has been determined for the protozoa Tetrahymena pyriformis (Yoshioka et al., 1985). This is the lowest available effect value which was determined for BHT.
It can be assumed that 2,6-di-tert-butyl-p-cresol is not toxic for soil microorganism up to the limit of water solubility.This conclusion is supported by a growth inhibition test on Bacillus subtilis(soil bacteria) where the 1h-EC50 was 22.04 mg/L, well-above the water solubility of the test subtance.
Key value for chemical safety assessment
Additional information
P. fluorescens is a bacteria which may be found in soil and water
Tetrahymena pyriformis is a protozoa . Protozoa are eukariotic cells and ubiquitous in the aquatic and terrestrial environment.
Photobacterium phosphoreum (Vibrio fischeri) is a bacteria which is found in symbioses with marine organisms.
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