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EC number: 203-643-7 | CAS number: 109-06-8
- 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
Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption
- Remarks:
- adsorption
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Published in peer reviewed literature, limitations in design and/or reporting but otherwise adequate for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Adsorption studies using gas-liquid chromatography-III. experimental factors influencing adsorption
- Author:
- Martin and Al-Bahrani
- Year:
- 1 978
- Bibliographic source:
- Water Rechearch Vol. 12. pp. 879 to 888 (1978)
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Article abstract by Martin and Al-Bahrani, 1978:
"Gas-liquid chromatography with a flame ionization detector system using the direct injection of aqueous solutions was used to monitor the adsorption of selected organic compounds in water onto activated carbon. The effects of changes in experimental factors influencing adsorption were investigated using both batch (agitated flask) and column (flow through packed bed) systems; solution pH and concentration, carbon particle size, carbon bed depth and flow rate were all studied. The direct injection of aqueous solutions was observed to facilitate the direct analysis of pollutants in water obviating the need for preliminary concentration or extraction steps." - GLP compliance:
- no
- Type of method:
- other: both batch (agitated flask) and column (flow through packed bed) systems
- Media:
- other: In water onto activated carbon
Test material
- Reference substance name:
- 2-methylpyridine
- EC Number:
- 203-643-7
- EC Name:
- 2-methylpyridine
- Cas Number:
- 109-06-8
- Molecular formula:
- C6H7N
- IUPAC Name:
- 2-methylpyridine
- Details on test material:
- - Name of test material (as cited in study report): 2-methylpyridine
Constituent 1
- Radiolabelling:
- no
Study design
HPLC method
- Details on study design: HPLC method:
- EQUIPMENT
Gas-liquid chromatography with a flame ionization detector system using the direct injection of the aqueous solution. A 1.5 m long. 3.175 mm diameter Teflon column packed with 15% Carbowax 20 M on 85 x 100 mesh Universal B was used for all the analyses (Universal B support. supplied by Phase Separations Ltd.).
MOBILE PHASES
Oxygen-free nitrogen was used as a carrier gas.
Batch equilibrium or other method
- Analytical monitoring:
- yes
- Details on matrix:
- Adsorption to Type CAL 12 x 40 (U.S. sieve series) granular activated carbon supplied by Chemviron Ltd. (formerly Pittsburgh Activated Carbon Ltd.) was measured.
- Details on test conditions:
- The adsorption capacity and adsorption rate were determined
Results and discussion
Any other information on results incl. tables
The authors conclusive summary is:
"The results of the studies may be summarised as follows:
- In a rapidly mixed batch system, the rate of adsorption was controlled by intraparticle diffusion. In column systems, for the most part, film diffusion appeared to be the rate-limiting step for the transfer or solute to the carbon.
- Both the ionised and neutral species of pyridine, 2-methylpyridine and o-cresol were adsorbed on activated carbon; the adsorption of ionised species was more affected by variation in solution pH. The pH effect on adsorption appeared to be mainly due to the competitive effect of hydrogen ions and acid adsorption and the effect of pH variation on the nature of the activated carbon surface.
- Decrease in particle size had no noticeable effect on the total carbon capacity for adsorption. In column systems, the realised carbon capacity for adsorption at breakpoint increased linearly with decrease in particle size.
- The rate of adsorption on carbon increased with decrease in carbon particle size. However, for a particle size below 0.4 mm, the rate or increase in uptake rate was considerably decreased which indicated that little would be gained by using carbon particles smaller than 0.4 mm. In the column system, the time required to reach the breakpoint increased linearly with decrease in particle size. After the breakpoint however, the approach to the exhaustion capacity of the carbon column speeded up with decreasing particle size.
- The rate of adsorption on carbon increased with increase in initial solution concentration. In the column system, the realised carbon capacity for 2-methylpyridine adsorption at breakpoint increased sharply with increase in initial concentration from 1.04 mg/L to 23.6 mg/L but was only slightly increased by a further increase in initial concentration.
- The breakpoint time of a carbon column varied with the carbon bed depth. Although the realised carbon capacity for adsorption at breakpoint increased at a decreasing rate with increase in carbon bed depth, the exhaustion capacity of the carbon column was not affected by the increase in bed depth.
- An increase in the flow rate through the carbon bed from 5.2 to 11.0 m3m-2h-1 had little effect on the rate of uptake of 2-methylpyridine on the carbon column.
- For single solute solutions, it was possible to predict the carbon column behaviour from results obtained in batch type experiments. (For solutions containing a complex mixture of organic material however, data obtained from batch type experiments could underestimate the capacity of the activated carbon for adsorption when used in column systems; Martin & Al-Bahrani, 1977.)
- Gas-liquid chromatography with a flame ionization detector system using the direct injection of aqueous solutions was found to be an excellent technique for monitoring the adsorption process for both mono and multi-solute solutions. The injection of aqueous solutions facilitates direct analysis of potential pollutants without the errors which inevitably accompany preliminary concentration or extraction steps. Rapidity, precision, convenience and a reasonable degree of sensitivity were all repeatedly observed; the monitoring of concentrations below 0.1 mg/L would necessitate a more sophisticated detection system such as mass spectrometry."
Applicant's summary and conclusion
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