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EC number: 233-713-2 | CAS number: 10326-41-7
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 130 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 85% CL = 100-180
- Details on results:
- The 24, 48 and 96 hour LC50 values for SY-83 were 140, 130 and 130 mg/L, respectively. All results were based on the nominal concentrations of 56, 100, 180, 320 and 560 mg/L. The no-effect concentration based on absence of mortality and abnormal effects after 96 hours of exposure was 56 mg/L.
An examination of the fish culture and acclimation records for this test indicated that the fish were in good condition for testing. The dissolved oxygen concentrations ranged from 5.6 to 9.0 mg/L during the test. These values represented 64 and 102 % saturation at 22 °C, respectively, and were considered adequate for testing. The pH values ranged from 3.1 to 7.2, with decreasing levels as test concentrations increased. - Results with reference substance (positive control):
- The bluegill sunfish were challenged with a reference compound, Antimycin A, to verify method precision. The 96 hour LC50 for bluegill sunfish exposed to Antimycin A was 1.0 × 10-4 mg/L and was within the 95 % confidence intervals reported in the literature.
- Validity criteria fulfilled:
- yes
- Remarks:
- Water quality parameters of temperature, dissolved oxygen and pH were measured throughout the test and were within acceptable limits.
- Conclusions:
- A test of the short-term toxicity of lactic acid (SY-83) to bluegill sunfish resulted in an LC50 of 130 mg/L (nominal).
- Executive summary:
The acute toxicity of lactic acid (SY-83) to bluegill sunfish (Lepomis macrochirus) was assessed using the methods outlined by the Committee on Methods for Toxicity Tests with Aquatic Organisms. Water quality parameters of temperature, dissolved oxygen and pH were measured throughout the test and were within acceptable limits. As a method precision check, the bluegill sunfish were challenged with a reference compound, Antimycin A. The estimated 96-hour LC50 and 95 % confidence limits (C.L.) were within the 95 % confidence limits reported in the literature. Culture and acclimation records indicated that the fish were in good condition for testing. The study was conducted at the following nominal concentrations of SY-83: 56, 100, 180, 320 and 560 mg/L. Ten fish, with a mean weight of 0.37 (± 0.15) g and a mean standard length of 24 (± 2.3) mm, were exposed to each test concentration and a blank control. The results of the four day static fish toxicity studies using lactic acid and Antimycin A are summarized below. The 24 and 48 hour LC50 values were also determined.
Lactic acid:
LC50(96 h) = 130 mg/L (95 % CI: 100–180 mg/L)
Antimycin A:
LC50 (96 h) = 1.0 × 10–4 mg/L (95 % CI: 0.75–1.4 × 10–4 mg/L)
Furthermore, the results indicate a 96-hour no-observed effect concentration of 56 mg/L, which was based on absence of mortality and abnormal effects.
This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 130 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95 % CL= 100-180
- Details on results:
- The 24, 48 and 96 hour LC50 values for SY-83 in the 96 hour static toxicity test with rainbow trout (Salmo gairdneri) were 150, 130 and 130 mg/L, respectively. All results were based on the nominal concentrations of 32, 56, 100, 180 and 320 mg/L. The no-effect concentration based on the lack of mortality and abnormal effects after 96 hours of exposure was 56 mg/L. The abnormal effects of mortality, surfacing and/or loss of equilibrium were observed in the 100, 180 and 320 mg/L test concentrations during the 96 hour exposure period.
The effects observed for positive control Antimycin A was within the 95% confidence intervals reported in the literature. An examination of the fish culture and acclimation records for this test indicated that the fish were in good condition for testing.
The dissolved oxygen concentrations ranged from 6.1 to 9.2 mg/L during the test. These values represented 56 and 85% saturation at 12°C, respectively, and were considered adequate for testing. The pH values ranged from 3.5 to 7.3. The pH values decreased with higher test concentrations.
The study was conducted following the intent of the Good Laboratory Practice Regulations and the final report was reviewed by Analytical Bio-Chemistry Laboratories' Quality Assurance Unit. All original raw data was provided to Union Oil Company, with a copy retained at Analytical Bio-Chemistry Laboratories. - Validity criteria fulfilled:
- yes
- Remarks:
- Water quality parameters of temperature, dissolved oxygen and pH were measured throughout the test and were within acceptable limits.
- Conclusions:
- The toxicity of lactic acid to rainbow trout was measured to be: LC50 (96h) 130 mg/L nominal concentration of test material.
- Executive summary:
The acute toxicity of lactic acid to rainbow trout (Oncorhynchus mykiss, fromerly known as Salmo gairdneri) was assessed using the methods outlined by the Committee on Methods for Toxicity Tests with Aquatic Organisms. Water quality parameters of temperature, dissolved oxygen and pH were measured throughout the test and were within acceptable limits. As a method precision check, the rainbow trout were challenged with a reference compound, Antimycin A. The estimated 96 hour LC50 and 95 % confidence limits (C.L.) were within the 95 % confidence limits reported in the literature. Culture and acclimation records indicated that the fish were in good condition for testing. The study was conducted at the following nominal concentrations of lactic acid: 32, 56, 100, 180 and 320 mg/L. Ten fish, with a mean weight of 1.09 (± 0.28) g and a mean standard length of 42 (± 3.4) mm, were exposed to each test concentration and a blank control. The results of the four day static fish toxicity studies on lactic acid and Antimycin A are summarised below. The 24 and 48 hour LC50 values were also determined.
Lactic acid:
LC50 (96 h) = 130 mg/L (95 % CI = 100–180 mg/L)
Antimycin A:
LC50 (96 h) = 4.8 × 10–5 mg/L (95 % CI = 2.4–7.5 × 10–5 mg/L)
Furthermore, the results indicate a 96-hour no-observed effect concentration for lactic acid of 56 mg/L, which is based on the absence of mortality and abnormal effects.
This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 180 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 320 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 195 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- yes
- Conclusions:
- The LC50 of L(+) lactic acid to Danio rerio was determined to be 195 mg/L (mean measured concentration).
- Executive summary:
The acute toxicity of the test substance, a solution of about 80% L(+) lactic acid, to the freshwater fish species Brachydanio rerio was determined according to OECD guideline no. 203 and under GLP. The study was carried out as a semi-static test with daily replacement of the test solutions and with 10 fish for each concentration. The exposure duration was 96 hours. The nominal concentrations tested were 100, 180, 320, 560 and 1000 mg/L. The test substance appeared to be completely dissolved at all concentrations tested (visually assessed). The actual concentrations of L(+) lactic acid were determined enzymatically with a Boehringer test kit. They were between 70 and 77% of nominal just after dosing (average 74%). To test the stability the concentrations of L(+) lactic acid were also analysed just before renewal and were between 56 and 82% of nominal (average 70%).
The results of the test were (as nominal concentrations):
96-h LC50= 320 mg/L
96-h LC100= 560 mg/L
96-h NOEC (mortality) = 180 mg/L
96-h LC50= 195 mg/L (mean measured concentration)
The nominal concentrations quoted in this report relate to the test material (a solution of about 80% L(+) lactic acid) as supplied by the sponsor. Toxic effects are probably caused by acidification, since test solutions were not buffered or neutralised.
This information is used in a read-across approach in the assessment of the target substance.For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 320 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95 % CL = 320-468
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- ca. 320 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- - Behavioural abnormalities: No data
- Observations on body length and weight: No data
- Other biological observations: No data
- Mortality of control: No data
- Other adverse effects control: No data
- Abnormal responses: No data
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: No data
- Effect concentrations exceeding solubility of substance in test medium: No - Reported statistics and error estimates:
- LC50, 95 % confidence interval (CI)
- Sublethal observations / clinical signs:
The apparent toxicity of lactic acid toD. reriocan be explained by the low pH values of the test substance solutions (pH 4.1 and 3.5 at concentrations of 320 and 560 mg/L, respectively).
- Validity criteria fulfilled:
- not specified
- Remarks:
- Poor documentation, validity cannot be assessed
- Conclusions:
- The short-term toxicity testing of lactic acid on freshwater fish (Danio rerio) resulted in an LC50 (96 h) of >320 mg/L (nominal), which can be attributed to a pH effect.
- Executive summary:
In a 96-h acute toxicity study, zebra fish (Danio rerio) were exposed to L-(+)-lactic acid at nominal concentrations of 0 (control), 320 and 560 mg/L (further information on the number of concentration levels not available) under semi-static conditions. The 96-h LC50 was > 320 mg/L. The observed effects can be attributed to a pH effect. The NOEC value, based on mortality effects, was 320 mg/L, respectively. Sublethal effects were not reported. Based on the results of this study, L-(+)-lactic acid would not be classified as hazardous to the aquatic environment according to the CLP Regulation (EC) No 1272/2008.
This toxicity study is classified as supplementary information and does not satisfy the guideline requirement for a fish short-term toxicity study but can nevertheless be used as supportive data or in a weight-of-evidence approach.
Results synopsis
Test organism: Zebra fish (Danio rerio)
Test type: Semi-static
LC50: > 320 mg/L
NOEC: 320 mg/L
Endpoint(s) effected: Survival/mortality
This information is used in a read-across approach in the assessment of the target substance.For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
Referenceopen allclose all
Description of key information
In short-term toxicity tests of lactic acid in three different fish species mortality was observed resulting in estimated LC50 values ranging between 130 and > 320 mg/L (nominal) which can be attributed to a pH effect. Lactate as such is considered not exert any systemic effects on fish in the tested concentration range of up to 560 mg/L.
Key value for chemical safety assessment
Additional information
In four studies on short-term toxicity of the read across substance L(+) lactic acid to fish (three different species: Danio rerio, Lepomis macrochirus, Oncorhynchus mykiss) mortality was observed resulting in estimated LC50 values ranging between 130 and > 320 mg/L (nominal). All studies are relatively poorly documented and therefore reliable only with restrictions. However, they can be used in a weight-of-evidence approach. In one of the studies (Bowmer et al., 1998) the observed mortality was explicitly attributed to pH effects: pH at the test concentrations of 320 and 560 mg/L was measured to be 4.1 and 3.5.
The theoretical pH shift caused by lactic acid at the lowest identified LC50 of 130 mg/L (= 1.443 mmol/L), considering a pKa of 3.9, would result in a final pH of 3.43. This compares quite well to the measured pH values of 4.1 and 3.5 at test concentrations of 320 and 560 mg/L in a slightly buffered system (Bowmer et al., 1998).
Therefore, the mortality observed in the available short-term toxicity tests on fish can undoubtfully be attributed to a pH shift instead of being a toxic effect of the lactate ion/molecule. Accordingly, since any toxic effects of the lactate are of interest instead of acidification it can be concluded that within the tested concentration range (up to 560 mg/L) lactic acid does not cause lethal effects on fish, except pH related mortality. A key value (LC50) for chemical safety assessment hence cannot be identified.
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