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EC number: 234-433-3 | CAS number: 12003-65-5
- 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, other
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Kd-values are based on reliable field data of concentration levels in pore water and sediment of rivers, which were highly exposed to untreated wastewater; no standard guideline test was conducted to generate Kd-values. Kd-values are calculated based on the hypothesis that equilibrium exists between the baseline levels in pore water and in sediment. LOD/LOQ were determined for each element, but values are not shown.
Data source
Reference
- Reference Type:
- publication
- Title:
- Content, distribution and fate of 33 elements in sediments of rivers receiving wastewater in Hanoi, Vietnam
- Author:
- Marcussen, H. et al.
- Year:
- 2 008
- Bibliographic source:
- Environ. Pollut. 155, 41-51
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Determination of the content and the distribution of 33 elements, including aluminium, in the sediment and pore water of the main wastewater receiving rivers in Hanoi, Vietnam. Distribution coefficients (log10 Kd) were calculated as the ratio between sediment and pore water concentrations of aluminium.
- GLP compliance:
- no
- Type of method:
- other: field data of aluminium levels in pore water and sediment
Test material
- Reference substance name:
- Aluminium
- EC Number:
- 231-072-3
- EC Name:
- Aluminium
- Cas Number:
- 7429-90-5
- Molecular formula:
- Al
- IUPAC Name:
- aluminium
Constituent 1
- Radiolabelling:
- no
Study design
- Test temperature:
- environmental relevant temperatures
Batch equilibrium or other method
- Analytical monitoring:
- yes
- Details on sampling:
- Sediment sampling:
- three sediment samples were collected in both rivers, three replicates were collected from each site
- sediment sampler: equipped with a polymethylmethacrylat inner liner (KC Denmark)
Sediment treatment in laboratory:
- under a N2 atmosphere sediment core samples were subdivided into 0-10 cm, 10-20 cm and 20-30 cm sections
Pore water collection:
- Sediment samples from the 0-10 cm section were transferred to a polypropylene (PP) Büchner funnel with a 25 µm mesh nylon filter
- extraction of minimum 15 ml pore water under suction of 10 kPa to a 50 ml PP tube
- filtration of 10 ml of the collected pore water through a 0.45 µm nylon filter (Millipore)
Sediment and pore water parameters:
- pH and redox potentials was determined in the pore water
Sample storage:
- acidified pore water samples and sediments were frozen and transported to Denmark for further treatment and analyses
- Details on matrix:
- - organic carbon content in sediments: 1.2-5.3% and 1.8-10.6% in the To Lich and Kim Nguu rivers, respectively
- pH: 7.4-8.1 in the pore water extracted from the upper 10 cm sediment of both rivers
- inorganic carbon in sediments: 0.02-2.12%
- redox potential in the pore water samples: -257 to -185 mV (highly reduced)
Results and discussion
Partition coefficients
- Key result
- Phase system:
- other: sediment-pore water
- Type:
- log Kp
- Value:
- 6.81 L/kg
- Matrix:
- sediment and pore water samples from all six sites
- Remarks on result:
- other: see 'Remarks'
- Remarks:
- Log Kp range for all six sites: 5.92-6.81 L/kg; sediment organic carbon concentration 1.2-5.3% and 1.8-10.6% in the To Lich and Kim Nguu river, respectively
Results: Batch equilibrium or other method
- Recovery of test material:
- 85-108%
- Transformation products:
- no
Any other information on results incl. tables
Mean and standard deviation (n=3) for sediment elemental aluminium concentrations (mg/kg dw sediment) in Kim Nguu river:
Depth | Site 1 | Site 2 | Site 3 |
0 -10 cm | 37 490 ± 4716 | 39 875 ± 2374 | 56 446 ± 13 168 |
10 -20 cm | 57 350 ± 7204 | 61 777 ± 15 707 | 47 658 ± 18 739 |
20 -30 cm | 53 492 ± 2619 | 41 870 ± 21 334 | 54 012 ± 30 252 |
Mean and standard deviation (n=3) for sediment elemental concentrations of aluminium (mg/kg dw sediment) in To Lich river:
Depth | Site 1 | Site 2 | Site 3 |
0 -10 cm | 41 334 ± 3752 | 62 138 ± 32 641 | 61 062 ± 18 526 |
10 -20 cm | 41 104 ± 4122 | 47 034 ± 386 | 55 381 ± 5618 |
20 -30 cm | 47 911 ± 7017 | 64 845 ± 9037 | 50 917 ± 30 611 |
Range for the elemental pore water concentration (µg/L) in both river sediments:
Al: (5.92 -26.5) x 103
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- Reliable levels of aluminium were determined in sediment and pore water samples of sediments from two rivers which were exposed to untreated wastewater in Hanoi, Vietnam. Sampling and analytical procedures are considered adequate and resulted in reliable data. Assuming equilibrium between the typical concentration in pore water and sediment, relevant Kd-values were generated. Data are therefore considered useful for the determination of a relevant Kd for the sediment compartment and log Kd values for all six locations in the rivers To Lich and Kim Nguu range from 5.92-6.81 L/kg.
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