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EC number: 201-557-4 | CAS number: 84-74-2
- 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 terrestrial plants
Administrative data
- Endpoint:
- toxicity to terrestrial plants
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: well documented and scientifically acceptable, but lacking testing guidelines
Cross-reference
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 983
- Report date:
- 1983
Materials and methods
- Principles of method if other than guideline:
- No guideline specified, cf. "Any other information on material and methods" for details.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Dibutyl phthalate
- EC Number:
- 201-557-4
- EC Name:
- Dibutyl phthalate
- Cas Number:
- 84-74-2
- Molecular formula:
- C16H22O4
- IUPAC Name:
- dibutyl phthalate
Constituent 1
Test organisms
- Species:
- other: Hordeum vulgare, Spinacea oleraceae
- Details on test organisms:
- Protoplasts were prepared from barley {Hordeum vulgare L. cv. Simba) according to Hampp and Ziegler (1980). Grains were soaked for 16 h in aerated running tap water, and grown in a mixture of peat and sand (Ryberg and Sundqvist 1976) in a climate chamber irradiated with white light (General Electric F72P617 CW, USA) at an intensity of 40 W m^-2 (16 h light/8 h dark, 16°C/14°C, relative humidity 85%/75%). Protoplasts were prepared from 7-day-old leaves, using leaf segments 3 cm long and taken 5 cm from the base of the leaves. The incubations with enzyme were made at 22°C instead of at 28°C in Hampp and Ziegler (1980).
Thylakoids were prepared from spinach (Spinacea oleraceae L.) grown in a climate chamber irradiated with white light (General Electric F72P617 CW, USA) at an light intensity of 40 W m^-2 (10 h light/14 h dark, 21°C/17°C, relative humidity 70%) for 5-8 weeks. Thylakoids were prepared according to Radosevich et al. (1979) with the modifications that the chloroplasts were osmotically disrupted in 0.1 M NaCl, and suspended in a medium containing 0.2 M sorbitol instead of 0.1 M. When IC50 was determined according to Tischer and Strotmann (1977), their method for preparing thylakoids lacking the coupling factor was used.
Results and discussion
Effect concentrationsopen allclose all
- Species:
- Hordeum vulgare
- Dose descriptor:
- other: IC50
- Effect conc.:
- 0 other: M
- Basis for effect:
- other: CO2 reduction
- Species:
- other: Spinacea oleraceae
- Dose descriptor:
- other: IC50
- Effect conc.:
- 0 other: M
- Basis for effect:
- other: electron transport
- Species:
- other: Spinacea oleraceae
- Dose descriptor:
- other: IC50
- Effect conc.:
- 0 other: M
- Basis for effect:
- other: uncoupled electron transport
Any other information on results incl. tables
The effect of DBP on photosynthesis in protoplasts prepared from barley
Protoplasts were used because we wanted to compare photosynthesis in higher plant with that of an alga, without interference by the long range transport of metabolites typical for higher plants. Photosynthesis was measured either as 14CO2-reduction or as CO2-dependent oxygen evolution. The chlorophyll concentrations were different in the two types of experiments (Tab. 1). DBP inhibited photosynthesis at concentrations higher than lO^-5 M (Fig. 3).
The effect of DBP on electron transport in isolated thylakoids from spinach
As photosynthesis was inhibited by DBP in both algae and protoplasts, we investigated in what photosynthetic system(s) the effect was localized. By choosing isolated thylakoids as a test system and by comparing the results obtained on different organisational levels (cells, protoplasts, thylakoids) we should be able to assign the effect of DBP to a certain level.
The effects of DBP on coupled and NH4CI-uncoupled basal electron transport in photosystem II + I are shown in Fig. 4. Electron transport was inhibited at DBP concentrations higher than 10^-4 M, the uncoupled system being the most sensitive system with an IC50 value of 3 X 10^-4. With a photosystem I assay (methylviologen as electron acceptor and dichlorophenolindophenol/ascorbate as electron donor couple) no effect was observed with DBP concentrations as high as 10^-3 (results not shown). Reactions in
photosystem II are thus being affected by DBP. In order to determine a chlorophyll independent IC50 value the method of Tischer and Strotmann (1977) was used. Here the ferricyanide dependent oxygen evolution in thylakoids devoid of coupling factor is measured at different chlorophyll concentration. By extrapolating to zero chlorophyll concentration the IC50 value in DBP treated thylakoids was found to be 2.5 x 10^-5 M.
Applicant's summary and conclusion
- Conclusions:
- The CO2-reduction in isolated protoplasts prepared from barley (Hordeum vulgare L. cv. Simba) was inhibited by phthalate. The IC50 value was 2 x 10^-4 M. The electron transport in isolated thylakoids prepared from spinach was inhibited with an IC50 value of 3 x 10^-4 M. The IC50 value for
uncoupled electron transport extrapolated to zero chlorophyll concentration was 2.5 X 10^-5 M. The effect of di-n-butyl phthalate was localized to reactions in photosystem II. Di-n-butyl phthalate could thus be a pollutant which affects growth and photosynthesis of plants. - Executive summary:
This is part of a study conducted on algae, barley and spinat. Only the effects on barley and spinach are documented here. Those on algae can be found under section 6.1.5.
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