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EC number: 701-024-0 | CAS number: 26038-87-9
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- Cyprinus carpio
- Details on test organisms:
- TEST ORGANISM
- Common name: Carp
- Strain:
- Source: Zodiac, proefacc, "De Haar Vissen", Wageningen
University and Research Centre, The Netherlands.
- Age at study initiation (mean and range, SD): No data
- Length at study initiation (length definition, mean, range and SD): Final test: 2.3 ± 0.1 cm
- Weight at study initiation (mean and range, SD): Final test: 0.29 ± 0.05 g
- Feeding during test: Daily with pelleted fish food (Cyprico Crumble
Excellent (300-500 um), Coppens International bv,
Helmond, The Netherlands)
ACCLIMATION
- Acclimation period: at least 12 days after delivery - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 20.7°C – 21.6°C
- pH:
- 7.6 - 8.0
- Dissolved oxygen:
- 6.1 - 8.6 mg/L
- Salinity:
- N/A
- Nominal and measured concentrations:
- Nominal: 100, 170, 320, 580, 1000 mg a.i./L
Measured: 147, 265, 476, 857, 1470 mg a.i./L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 10 litres, all-glass, containing 9.8 litres of test solution
- Aeration: The test media were not aerated during the test.
- No. of organisms per vessel: 7 per concentration
Adjusted ISO medium, formulated using RO-water
(tap-water purified by reverse osmosis; GEON
Waterbehandeling, Berkel-Enschot, The Netherlands)
with the following composition:
CaCl2.2H2O 211.5 mg/l
MgSO4.7H2O 88.8 mg/l
NaHCO3 46.7 mg/l
KCl 4.2 mg/l
OTHER TEST CONDITIONS
- Photoperiod: 16 hours photoperiod daily
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
TEST CONCENTRATIONS
- Test concentrations: 100, 170, 320, 580, 1000 mg a.i./L - Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 617 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95% CL 529 - 823 mg a.i./L
- Details on results:
- - Behavioural abnormalities: Fins contracted against the body, caudal fin closed. Fins slightly reddish with clearly enlarged blood vessels. Enhanced respiratory rate. Swimming at the surface (only at 48 hour of exposure)
- Mortality of control: 0 - Conclusions:
- Under the conditions of the present test MEA Polyborate 1:3 induced no visible and or lethal effects in carp at nominally 320 mg a.i./l (NOEC).
The 96h-LC50 was 617 mg a.i./l based on nominal concentrations (95% confidence interval between 529 and 823 mg a.i./l). No 24, 48 or 72h-LC50 could be calculated (LC50 > maximum concentration tested). This value is used as an estimate of the short-term or acute toxicity of the test substance, per the OECD guidelines. - Executive summary:
96-Hour Acute Toxicity Study in Carp with MEA Polyborate 1:3. The study procedure described in this report was based on the OECD guideline No. 203, 1992. In addition, the procedures were designed to meet the test methods of the Commission Regulation (EC) No 440/2008, Part C.1, 2008 and the ISO International Standard 7346-1: Static method. MEA Polyborate 1:3, is a complex UVCB (Substance of Unknown or Variable composition or Complex reaction products and Biological materials) containing salt and non-salt compounds in rapid equilibrium. The test substance is prepared from monoethanolamine, borate compounds and water and contains 68% active ingredients/non-water components. The test substance was completely soluble in test medium at the concentrations tested. Preparation started with a concentration of 1000 mg active ingredient (a.i.)/l which corresponds to 1470 mg MEA Polyborate 1:3 per litre. No other treatment than magnetic stirring was needed to completely dissolve the test substance. The pH of the highest concentration was adjusted with 1M HCl. The lower test concentrations were prepared by subsequent dilutions of the highest concentration in test medium. A final test was performed based on the result of the range-finding test. Seven fish per group were exposed to a control and concentrations of 100, 170, 320, 580 and 1000 mg a.i./l corresponding to 147, 265, 476, 857 and 1470 mg MEA Polyborate 1:3 per litre, respectively. The total exposure time was 96 hours and samples for analytical confirmation of test concentrations were taken at the start and at the end of the test. Analyses were performed on samples taken from the nominal concentrations of 476, 857 and 1470 mg/l (i.e. 320, 580 and 1000 mg a.i./l). The concentrations of both boron and MEA were determined. Boron analyses: The corresponding nominal concentrations of boron in analysed samples were 55, 99 and 171 mg boron per litre, respectively. Analysis of the samples taken at the start of the final test showed that the actual concentrations were in agreement with nominal, 78-85% of nominal (note that the mean recoveries of the procedural recovery samples were between 83-88%). The measured concentrations remained stable during the entire test period (96-103% of initial). MEA analyses: The corresponding nominal concentrations of MEA in analysed samples were 81,146 and 250 mg MEA per litre, respectively. Analysis of the samples taken at the start of the final test showed that the actual concentrations were in agreement with nominal, i.e 118-125% of nominal and remained stable during the entire test period (95-102% of initial). Based on these results, the effect concentrations were expressed in terms of the nominal concentrations of the active ingredient. The study met the acceptability criteria prescribed by the protocol and was considered valid. The 96h-LC50 for MEA Polyborate 1:3 was 617 mg a.i./l based on nominal concentrations (95% confidence interval between 529 and 823 mg a.i./l). No mortalities were observed at 2, 24 and 48 hours, so no LC50 could be estimated. The maximum mortality observed at 72 hours was less than 50%, no LC50 could be determined.
Reference
Description of key information
Under the conditions of the present test MEA Polyborate 1:3 induced no visible and or lethal effects in carp at nominally 320 mg a.i./l (NOEC).
The 96h-LC50 was 617 mg a.i./l based on nominal concentrations (95% confidence interval between 529 and 823 mg a.i./l). No 24, 48 or 72h-LC50 could be calculated (LC50 > maximum concentration tested). This value is used as an estimate of the short-term or acute toxicity of the test substance, per the OECD guidelines.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 617 mg/L
Additional information
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