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EC number: 205-758-8 | CAS number: 150-38-9
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 29-30 June 2000
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study according to guideline and under GLP, some data on identity and purity, batch no. given but no CoA attached. Some phys-chem properties, no actual concentrations. When data on composition >=99.9%, reliability can be considered 2 (reliable with restrictions).
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- Principles of method if other than guideline:
- No actual concentrations measured
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- The synthetic sewage feed was made by dissolving the following amounts of substances in one liter of deionized water: 16 g peptone, 11 g meat extract, 3 g urea, 0.7 g NaCI, 0.4 g CaCI2.2.H20, 0.2 g MgS04.7H20, 2.8 g K2HP04. The EDTA and 3.5-dichlorophenol were added to the incubation vessels using stock solutions of 1.0 and 0.5 g/L, respectively. The stock solution of 3.5-dichlorophenol was prepared by dissolving 0.05 g 3.5-dichlorophenol in 1 ml of I M NaOH diluting to approximately 30 ml with deionized water, adding under stirring 0.5 M H2S04 to the point of incipient precipitation and finally diluting the mixture to 0.1 liter with deionized water (deviation of study plan; 100 ml prepared instead of 1 litre) . The stock solution of EDTA was prepared by adding 1.33 g Na2H2EDTA 2 H20 and 0.525 g CaCl2 2 H20 to approximately 900 mL of deionized water. The pH of this solution was titrated to 6.8 with a 1 N NaOH solution. Finally this mixture was diluted to 1 litre. The concentration H4EDTA in this solution was 1 g/L.
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- Secondary activated sludge was obtained from the WVVTP Nieuwgraaf in Duiven (2000.06.29). The WWTP Nieuwgraaf is an activated sludge plant treating predominantly domestic waste water. Prior to use the activated sludge was diluted with tap water (1.5x) and homogenized for two minutes in a lab blender 400. The dry weight of the activated sludge in the incubation vessels was 1.1 g/L.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 30 min
- Post exposure observation period:
- None
- Hardness:
- No specific data
- Test temperature:
- 21 °C
- pH:
- 7.1 - 7.5
- Dissolved oxygen:
- Is parameter of interest in this study
- Nominal and measured concentrations:
- Nominal concentrations: 125-250-500 mg/L expressed as H4EDTA
- Details on test conditions:
- The test was performed in 250 to 300 ml Erlenmeyers. The homogenized activated sludge was incubated in a shaking water bath (100 Hz, 20°C) for 30 minutes with various concentrations of the test compound and synthetic sewage.
The respiration rates of the activated sludge were measured in a biological Oxygen Monitor YSI 5300 (Yellow Springs Instruments, Ohio, USA). The BOM consisted of a thermostated vessel with a magnetic stirrer and an oxygen electrode. The electrode to measure the oxygen depletion tightly closed the vessel. The volume of the vessel was 10 ml and the temperature in the vessel was 20°C. The pH was measured using a Consort pH meter (Salm en Kipp BV, Breukelen, The Netherlands). The temperature was measured with a thermometer. The dry weight of the inoculum was determined by filtrating 100 ml of the activated sludge over a preweighed 12 um Schleicher and Schull filter. This filter was dried for 1.5 hours at 104°C and
weighed after cooling. Dry weight was calculated by subtracting the weighed filters. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Duration:
- 30 min
- Dose descriptor:
- EC50
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Remarks:
- H4EDTA
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- Only minor (5%) inhibition of the respiration was observed in the medium dose level (250 mg/L).
In the 125 and 500 mg/L minor (5-8%) stimulation was observed. - Results with reference substance (positive control):
- Inhibition was dose dependent, with an EC50 of 6.4 mg/L, within prescribed range (5-30 mg/L) for an exposure of 3 hours.
- Reported statistics and error estimates:
- The EC values were computed from the best fitted line (least square method) through the points given by the probit of the percentage inhibition and the logarithm of the concentration of the substance. All computations were performed with the program TOXCALC(TM) on a personal computer.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Restrictions as to composition of test material, no CoA. Study well performed, results are valid. EC50 (> 500 mg/L) can therefore be considered reliable.
- Executive summary:
An activated sludge respiration inhibition test was performed. The toxicity to activated sludge was determined in accordance with OECD Test Guideline 209, and in compliance with the OECD principles of Good Laboratory Practice. The test is valid as shown by the EC50 of the reference compound, 3,5dichlorophenol (6.4 mg/L) and control respiration rates which are within 15% of each other. The toxicity of EDTA to activated sludge was determined by measuring the respiration rate after a contact time of 30 minutes at various concentrations of the test substance (125 -500 mg/L). The inhibitory effect of EDTA at a particular concentration was expressed as a percentage of the two controls. From the results it is clear, that EDTA does not significantly inhibit the respiration of activated sludge up to a nominal concentration of 500 mg/L. EC20, EC50, EC80 >500 mg/L.
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Peer-reviewed data from EU Risk Assessment Report
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- Equimolar amounts of CaCl2 were added, thus CaEDTA was formed in the stock solutions.
- Test organisms (species):
- activated sludge, domestic
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 30 min
- Nominal and measured concentrations:
- Na2H2EDTA was used in concentrations of 125, 250, and 500 mg/L (referred as H4EDTA).
- Details on test conditions:
- Type: aquatic
- Duration:
- 30 min
- Dose descriptor:
- other: EC20
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 30 min
- Dose descriptor:
- EC10
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- At the highest test concentration (500 mg/L) a significant inhibition of the respiration rate could not be detected after 30 minutes. It can be concluded that both the EC10 and NOEC values are above 500 mg/L.
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Remarks:
- Summary of available data used for the endpoint assessment of the target substance.
- Adequacy of study:
- key study
- Justification for type of information:
- Refer to the Analogue Approach Justification document provided in Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 30 min
- Dose descriptor:
- EC50
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Remarks:
- H4EDTA
- Basis for effect:
- inhibition of total respiration
- Remarks on result:
- other: RA-A, CAS 139-33-3, van Ginkel & Stroo, 2000, Respiration inhibition, 3 h, RL2
- Duration:
- 30 min
- Dose descriptor:
- EC10
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks on result:
- other: RA-A, CAS 139-33-3, van Ginkel & Stroo, 2004, Respiration inhibition, 30 min, RL2
- Endpoint:
- activated sludge nitrification inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- no data available
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: acceptable, well documented study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Nitrification inhibition was evaluated in 24 h batch extant respirometric assays employing biomass from a continuously operated nitrifying enrichment reactor.
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- aerobic microorganisms
- Test type:
- static
- Water media type:
- not specified
- Limit test:
- no
- Total exposure duration:
- 24 h
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.4 mmol/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: nitrification inhibition
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The concentration causing 50% inhibition was estimated at 2.4 mM/L for EDTA. Inhibition by EDTA reached its ultimate value within 6 h.
- Executive summary:
In a 24 h nitrification inhibition test the EC50 of EDTA to microorganism from a continuously operated nitrifying enrichment reactor was determined to be 2.4 mM/L.
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Test procedure according to international standards (ISO)
- Qualifier:
- according to guideline
- Guideline:
- ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
- GLP compliance:
- no
- Specific details on test material used for the study:
- OTHER SPECIFICS
Purity/content: 40 % test substance, 55 % water, 5 % salts - Analytical monitoring:
- no
- Test organisms (species):
- activated sludge, industrial
- Details on inoculum:
- The activated sludge inoculum used in this study originated from an industrial wastewater treatment plant (BASF AG). The concentration of dry substance was 1 g/L.
- Test type:
- static
- Water media type:
- freshwater
- Details on test conditions:
- Type: aquatic
- Duration:
- 30 min
- Dose descriptor:
- other: EC20
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Key result
- Duration:
- 30 min
- Dose descriptor:
- EC10
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
Referenceopen allclose all
Concentration (mg/L) |
Activity mg O2/L min |
% inhibition |
Control |
0.29 |
- |
Control |
0.28 |
- |
125 |
0.31 |
0 (-9) |
250 |
0.27 |
5 |
500 |
0.30 |
0 (-5) |
Respiration inhibition at 1000 mg/L: 4.4 %
EC20 (relating to test compound) > 400 mg/L
Description of key information
In conclusion EDTA species are of low toxicity to (activated sludge) microorganisms and the degradation process in sewage treatment plants is not expected to be inhibited.
Key value for chemical safety assessment
Additional information
Since no studies investigating the toxicity trisodium hydrogen EDTA (CAS 150-38-9) to activated sludge microorganisms are available, in accordance to Regulation (EC) No 1907/2006 Annex XI, 1.5 a read-across to structurally related EDTA species was conducted. This read-across is justified in detail in the overall summary (IUCLID Section 6.1) and within the analogue justification in IUCLID Section 13.
For the assessment of toxicity to microorganisms data from the source substances disodium dihydrogen EDTA (CAS 139-33-3), edetic acid (CAS 60-00-4) and tetrasodium EDTA (CAS 64-02-8) were used.
The first study (van Ginkel, 2000) with the source substance
disodium dihydrogen EDTA the toxicity towards activated sludge
microorganisms was determined in accordance with OECD 209 (GLP). The
toxicity of the substance to activated sludge was determined by
measuring the respiration rate after a contact time of 30 min at various
concentrations of the test substance (125 -500 mg/L based on H4-EDTA).
Equimolar amounts of CaCl2 were added, thus Ca-EDTA was formed in the
stock solutions. From the results it is clear, that the substance does
not significantly inhibit the respiration of activated sludge
microorganisms up to a nominal concentration of 500 mg/L resulting in an
EC50 (30 min) > 500 mg/L. The test is valid as shown by the EC50 of the
reference compound, 3,5-dichlorophenol of 6.4 mg/L and control
respiration rates which are within 15%.
This result is supported by an additional study with the same substance
under comparable test conditions (van Ginkel, 2004). In this study the
same EC50 (30 min) of > 500 mg/L resulted.
Both results are supported by a study performed according to ISO 8192 with the source substance tetrasodium EDTA. Activated sludge from an industrial sewage treatment plant did not cause inhibition of total respiration resulting in an EC10 (30 min) of > 1000 mg/L (nominal).
An additional study is available investigating the effects of edetic acid on nitrification by microorganisms (Hu et al, 2003). In the 24 h nitrification inhibition test the EC50 of H4-EDTA to microorganism was determined to be 2.4 mM/L, which is equivalent to 700 mg/L. The study did not follow a standard guideline but the result indicates a low toxicity to nitrifying microorganisms.
In conclusion EDTA species are of low toxicity to (activated sludge) microorganisms and the degradation process in sewage treatment plants is not expected to be inhibited.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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