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EC number: 240-178-9 | CAS number: 16039-53-5
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Outdated test guideline, not fully suitable for assessing ready biodegradability according to recent standards. Conduct of test valid according to guidelines applicable at that time, hence reliable with restrictions and used as supportive data.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.5 (Degradation: Biochemical Oxygen Demand)
- Version / remarks:
- Cited as Directive 84/449/EEC, C.8, and NEN 6634
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.6 (Degradation: Chemical Oxygen Demand)
- Version / remarks:
- Cited as Directive 84/449/EEC, C.9, and NEN 6633
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- A sample of activated sludge was taken from an oxidation ditch situated on the premises of TNO, Delft, The Netherlands. The oxidation ditch is used to treat domestic sewage. The original sludge (containing 3.5-4.0 g of solid substance.l'l) was allowed to settle for 4-8 minutes and 2 ml of the supernatant was used to inoculate each litre of BOD dilution water (ref. 1). The dilution water was aerated vigorously before use.
- Duration of test (contact time):
- ca. 20 d
- Initial conc.:
- 0 mg/L
- Initial conc.:
- 2 mg/L
- Initial conc.:
- 4
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- The BOD determination was conducted as described in the protocol, developed mainly from the Dutch Guideline 'Water-Determination of Biochemical Oxygen Demand after n days (BODn)' (NEN 6634). Test concentrations of 2.0 and 4.0 mg/l were prepared by adding respectively 33 and 66 ml of the 199.6 mg/l stock solution to 3.3 l lots of inoculated BOD dilution water. In order to check the activity of the inoculum and the possible toxicity of the test sub- stance, l ml/l1 of a solution containing 3 g/l of glucose and 3 g/l of glutamic acid, and this mixture with 4 mg/l of L(+) lactic acid were also tested.
Nitrification control was included by adding 2.5 mg/l of allylthiourea to bottles containing 2 mg\l of L(+) lactic acid. Quadruplicate BOD bottles were incubated at 20°C for 20 days. The COD was determined with two samples of l ml from a solution of 405.7 mg of test substance in 100 ml of Milli-Q water, and conducted as detailed in the Dutch Guideline. - Reference substance:
- other: Glucose
- Reference substance:
- other: Glutamic acid
- Reference substance:
- other: Allyl thiourea
- Test performance:
- The oxygen concentrations measured in the various bottles of the BOD determination are given in Annex B and discussed in detail in sections 3.1 and 3.2. Table l lists the mean oxygen concentrations measured and the oxygen consumption and BOD values calculated for L(-i-) lactic acid (referring to the test substance as such, containing 80 % L-(+)-lactic acid).
The pH of the medium in the BOD bottles was 7.0-7.1 at the start of the test, 6.6-6.9 after twenty days. The pH values in bottles with glucose added were generally lower 6.1-6.3. The temperatures measured in the BOD bottles varied between 19.9 and 20.7 °C. - Parameter:
- % degradation (O2 consumption)
- Value:
- 50
- Sampling time:
- 5 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 67
- Sampling time:
- 20 d
- Details on results:
- The BOD5 and BOD20 values of the various concentrations of L-(+)-lactic acid were in the ranges 0.44-0.45 mg O2/L and 0.54-0.60 mg O2/L, respectively; it was therefore concluded that the BOD5 and BOD20 of L-(+)-lactic acid are 0.45 and 0.60 mg O2/mg, respectively.
Similar oxygen consumption by the test substance was also found in the presence of glucose and glutamic acid, confirming these results. The COD value of L-(+)-lactic acid was found to be 0.902 mg O2/mg (duplicate values: 0.873 and 0.930 mg O2/mg). The theoretical oxygen demand was calculated tobe 0.85 mg O2/mg.
Comparison of the BOD and COD values indicates that degradation was about 50 % after 5 days and about 67 % after 20 days. - Parameter:
- BOD5
- Value:
- 0.45 g O2/g test mat.
- Parameter:
- COD
- Value:
- 0.9 g O2/g test mat.
- Parameter:
- BOD5*100/COD
- Value:
- 50
- Results with reference substance:
- The BOD5 and BOD20 values of the glucose/glutamic acid control were 3.02 mg O2/L and 7.29 mg O2/L respectively; these values indicate that the activity of the inoculum was not quite sufficient. According to ref. (3) a 150 mg/L glucose/glutamic acid mixture should have a BOD5 value of 200 ± 37 mg O2/L; this cor- responds to a value of 4.0 ± 0.75 mg O2/L for a 3 mg/L mixture. Since the BOD values were similar at both test substance concentrations and only slightly lower than the value found in the presence of glucose/glutamic acid with its higher microbial activity, the test was regarded as valid.
The results obtained by adding allylthiourea showed that some nitrification had taken place. - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable, but failing 10-day window
- Conclusions:
- With a BOD5 of 50 % and BOD20 of 67 % of COD, and considering the function of lactic acid in biological systems, it can be concluded that lactic acid is readily biodegradable. Since following an outdated and not fully adequate test guideline, the study is used as supportive data.
- Executive summary:
BOD (Biochemical Oxygen Demand) and COD (Chemical Oxygen Demand) determinations were carried out for L-(+)-lactic acid using the method described in the Dutch guidelines 'Water – Determination of Biochemical Oxygen Demand after n days (BODn)' (NEN 6634) and 'Water – Determination of Chemical Oxygen Demand (COD)' (NEN 6633), respectively. These methods are similar to those referred to in the EC test guidelines C.5 and C.6 (Regulation (EC) No 440/2008). The study was carried out in accordance with the OECD principles of Good Laboratory Practice.
The test substance was a pure chemical with a high solubility in water. Two concentrations (2 and 4 mg/L) were tested. An inoculum was prepared from activated sludge. lts microbial activity appeared to be sufficient although the control substances glucose and glutamic acid had a BOD5 of slightly less than the required value of 4.00 ± 0.75 mg O2/L.
No toxic effects were found.
The BOD5 of L-(+)-lactic acid was 0.45 mg O2/mg and the BOD20 was 0.60 mg O2/mg; the COD was 0.90 mg O2/mg. These figures indicate a degradation of 50 and 67 % after 5 and 20 days, respectively.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Outdated test guideline, not fully suitable for assessing ready biodegradability according to recent standards. Publication with relatively poor documentation of methodology and test condtitions.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.5 (Degradation: Biochemical Oxygen Demand)
- Version / remarks:
- Cited as Directive 92/69/EEC, C.5
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Duration of test (contact time):
- 20 d
- Initial conc.:
- 4 mg/L
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on results:
- BOD 20 = 0.60 mg O2 per mg test substance
- Parameter:
- BOD5
- Value:
- 0.45 g O2/g test mat.
- Parameter:
- COD
- Value:
- 0.85 g O2/g test mat.
- Parameter:
- BOD5*100/COD
- Value:
- 50
- Validity criteria fulfilled:
- not applicable
- Interpretation of results:
- readily biodegradable, but failing 10-day window
- Conclusions:
- Lactic acid is considered to be readily biodegradable. In view of methodological limitations, this study is used as supportive data.
- Executive summary:
The biodegradation of lactic acid and lactate esters was studied. The aim of the study was to provide predicted environmental data for additional alkyl homologues and metal salts. Lactic acid and its alkyl esters were degraded by more than 60 % in the ready biodegradability tests and from the data presented it is evident that lactic acid and the majority of alkyl lactates are readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Remarks:
- Validated QSAR model, acceptable in a regulatory context.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- according to guideline
- Guideline:
- other: REACH guidance on information requirements and chemical safety assessment, chapter R.6: QSARs and grouping of chemicals, May 2008.
- Principles of method if other than guideline:
- (Q)SAR calculation
- GLP compliance:
- no
- Parameter:
- other: Primary and ultimate biodegradability prediction: YES
- Remarks on result:
- other: QSAR calculation (BIOWIN)
- Details on results:
- Biowin1 (Linear Biodeg Probability) 0.9361
Biowin2 (Non-Linear Biodeg Probability) 0.9704
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
Biowin3 (Survey Model - Ultimate Biodeg) 3.5247
Biowin4 (Survey Model - Primary Biodeg) 4.2328
Result Classification: 5.00 -> hours 4.00 -> days 3.00 -> weeks
(Primary & Ultimate) 2.00 -> months 1.00 -> longer
Biowin5 (MITI Linear Biodeg Probability) 0.7362
Biowin6 (MITI Non-Linear Biodeg Probability) 0.8791
A Probability Greater Than or Equal to 0.5 indicates --> Readily Degradable
A Probability Less Than 0.5 indicates --> NOT Readily Degradable
Biowin7 (Anaerobic Linear Biodeg Prob) 0.9102
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast - Validity criteria fulfilled:
- not applicable
- Interpretation of results:
- readily biodegradable
- Conclusions:
- L-(+)-lactic acid is predicted to be readily biodegradable by the (Q)SAR model BIOWIN v4.10.
- Executive summary:
L-(+)-lactic acid is predicted to be readily biodegradable by the (Q)SAR model BIOWIN v4.10.
Referenceopen allclose all
Description of key information
Lactic acid/free lactate is considered to be readily biodegradable. The principle of ready biodegradability is extrapolated to zinc lactate by read-across.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Lactic acid is predicted to be readily biodegradable by the validated QSAR model BIOWIN v4.10. Supportive experimental studies (BOD5 and COD measurements) not satisfying recent standards for ready biodegradability tests allow the conclusion that lactic acid is readily biodegradable not satisfying the 10-d window criterion. It is generally established textbook knowledge that lactic acid, due to its biological function, is readily metabolised by practically all life-forms. Overall, lactic acid can be considered to be readily biodegradable. This conclusion is extrapolated to zinc lactate by read-across.
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