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EC number: 204-873-0 | CAS number: 127-95-7
- 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
Biodegradation in water and sediment: simulation tests
Administrative data
- Endpoint:
- biodegradation in water: sediment simulation testing
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- no data
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- In this literature publication, the materials and methods and results are sufficiently reported. The aim of the study is to demonstrate the presence of oxalate in plants and sediments and the occurrence of anaerobic microbial degradation in aquatic habitats, therefore the mineralization rates are presented as the rate of product formed (14CO2).
Data source
Reference
- Reference Type:
- publication
- Title:
- Anaerobic oxalate degradation: widespread natural occurence in aquatic systems
- Author:
- Smith, R.L., Oremland, R.S.
- Year:
- 1 983
- Bibliographic source:
- Applied and Environmental Microbiology, Vol. 46, No. 1, p. 106-113
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Mineralization of [14C]oxalate in sediment was measured using sediment from three different lakes.
Additional experiments: the oxalate content in several aquatic plants was determined, and degradation of oxalate present in aquatic plants was measured using litter bag experiments. - GLP compliance:
- not specified
Test material
- Reference substance name:
- Oxalic acid
- EC Number:
- 205-634-3
- EC Name:
- Oxalic acid
- Cas Number:
- 144-62-7
- IUPAC Name:
- oxalic acid
- Details on test material:
- Mineralization experiment:
- Name of test material (as cited in study report): [14C]oxalate
- Physical state: N2 sparged solution
- Specific activity (if radiolabelling): 50 Ci/mol
- Source: New England Nuclear
Litter bag experiment:
-Name of test material: oxalate naturally present in aquatic plants
Constituent 1
- Radiolabelling:
- yes
Study design
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- natural sediment
- Duration of test (contact time):
- ca. 6.5 h
Initial test substance concentration
- Initial conc.:
- ca. 3.6 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CH4 evolution
- CO2 evolution
- test mat. analysis
Results and discussion
Half-life of parent compound / 50% disappearance time (DT50)
- Remarks on result:
- other: no data
- Other kinetic parameters:
- pseudo-first order rate constant
- other: turnover time (1/rate constant) can be substantially less than 1 day
- Transformation products:
- not specified
Identity of transformation productsopen allclose all
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- CO2
- Identifier:
- common name
- Identity:
- CO2
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- methane
- Inventory number:
- InventoryMultipleMappingImpl [inventoryEntryValue=EC 200-812-7]
- CAS number:
- 74-82-8
Any other information on results incl. tables
The production rates of 14CO2 in anaerobic sediments amended with [14C]oxalic acid are summarized in the following table (reproduced from the publication).
Sediment sample (type) |
Total sediment oxalate concentration (µmol/liter of sediment) |
Oxalate mineralization rate (µCi of 14CO2 produced/liter of sediment/day) |
Rate constant (per day) |
Searsville Lake, eutrophic reservoir |
|||
Pelagic SVL |
688 |
27.3 |
0.55 |
15.4 |
0.31 |
||
Littoral SVL |
533 |
272.7 |
5.45 |
86.3 |
1.73 |
||
Intermediate SVL |
98.2 |
1.96 |
|
Big Soda Lake |
|||
Pelagic BSL |
100 |
0.2 |
0.004 |
Littoral BSL |
110 |
10.8 |
0.22 |
San Fransisco Bay, tidal mud flat |
|||
Salt marsh |
367 |
20.6 |
0.41 |
46.2 |
0.92 |
||
Tidal mud flat |
235 |
37.8 |
0.76 |
lake Tahoe, oligotrophic lake |
|||
Pelagic LT |
78 |
0.54 |
0.01 |
Near shore LT |
297 |
6.62 |
0.13 |
The following table contains the oxalate content of potential detrital inputs to aquatic sediments, and is also reproduced from the publication.
Sample |
Description |
% oxalic acid by dry wt |
Brown hickory |
Senescent leaves |
5.01 |
Brown oak |
Senescent leaves |
2.22 |
Sea grass (Zostera sp.) |
Whole plant |
1.02 |
Pickle grass (Salicornia sp.) |
Leaves |
1.99 |
Cord grass (Spartina sp.) |
Whole plant |
0.08 |
Waterlily (Nuphar sp.) |
Leaf blades |
3.34 |
Petioles |
5.02 |
|
Water milfoil (Myriophyllum sp.) |
Whole plant |
2.54 |
Widgeon grass (Ruppia sp.) |
Whole plant |
0.07 |
Algal mat |
Littoral zone ( ) |
0.21 |
Seston |
Pelagic zone ( ) |
0.04 |
The oxalate content in litter bags containing Myriophyllum sp samples decreased with time when burien in littoral sediment. The net loss was the result of a decrease in both the total plant mass remaining in the litter bag and the oxalate concentration of that plant material (7% of the initial total oxalate remained in the litter bag after 175 days, compared to 16% of the initial plant mass). In the litter bags placed in the aerobic water column, the exalate content remained relatively constant. The oxalate concentration of the litter bag contents was 2.54 mg/g dry wt initially, and after 175 days 2.06 mg/g dry wt for the water column-placed litter bags and 0.75 for the sediment-placed litter bags.
Applicant's summary and conclusion
Validity criteria
- Validity criteria fulfilled:
- not specified
- Conclusions:
- [14C]oxalic acid was anaerobically degraded to 14CO2 and traces of CH4 in all sediment types tested. In littoral and near-shore sediments the rate of 14CO2 production ranged from 6.6 to 273 µCi of 14CO2 produced/liter of sediment/day, and in pelagic sediments the rate was 0.2 to 27.3 µCi of 14CO2 produced/liter of sediment/day, under the current test conditions. The turnover time of the added [14C]oxalate can be substantially less than 1 day in some sediments.
- Executive summary:
The anaerobic degradation of oxalate was determined in different sediment samples. [14C]oxalic acid was anaerobically degraded to 14CO2 in all sediment types tested. In littoral and near-shore sediments the rate of 14CO2 production ranged from 6.6 to 273 µCi of 14CO2 produced/liter of sediment/day, and in pelagic sediments the rate was 0.2 to 27.3 µCi of 14CO2 produced/liter of sediment/day. Rate constants were 0.01 to 0.5 per day in pelagic sediments and 0.13 to 5.4 per day in littoral sediments. The turnover time of the added [14C]oxalate was less than 1 day in the sediment from the Searsville Lake.
The anaerobic degradation of oxalate appears to be a widespread phenomenon, occurring in every sediment tested.
The oxalate concentration of several plant species which are potential detrital inputs to the tested aquatic sedmients ranged from 0.1 to 5.0% (dw). In experiments with litter bags, the oxalate content of Myriophyllum sp. samples buried in freshwater littoral sediments decreased to 7% of the original value in 175 days.
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