Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Environmental fate & pathways

Biodegradation in water: screening tests

Currently viewing:

Administrative data

Link to relevant study record(s)

Reference
Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Acceptable well documented report; Study conducted according to guideline in compliance with GLP
Qualifier:
according to guideline
Guideline:
EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
Version / remarks:
Cited as Directive 92/69/EEC, C.4-E
GLP compliance:
not specified
Remarks:
GLP compliant study cited by SIDS 2004, report date is not given
Oxygen conditions:
aerobic
Inoculum or test system:
other: secondary effluent of a municipal sewage plant (Breisgauer Bucht, 500000 population equivalent), 0.4 mL/L
Duration of test (contact time):
28 d
Initial conc.:
3 mg/L
Based on:
test mat.
Reference substance:
acetic acid, sodium salt
Parameter:
other: % ThOD
Remarks:
theoretical oxygen demand
Value:
89
Sampling time:
28 d
Details on results:
Blanks:

Maximum deviation between parallels = 8.9%
Oxygen consumption after 28 days = 0.79-1.18 mg/L
pH : 7.2 at the beginning and 6.7 at the end of the test

----------------------------------
Sodium gluconate:

Maximum deviation between parallels = 4.6% at day 3
Biological degradation : 61% of ThOD after 3 days
Maximum degradation = 89% of the ThOD at day 28
pH : 7.2 at the beginning and 6.7 at the end of the test

Oxygen concentration during test never felt below 5.9 mg/lL.
----------------------------------------
Reference item (sodium acetate):

Maximum deviation between parallels = 3.8% at day 14.
Biological degradation : 67% after 3 days
pH : 7.2 at the beginning and 6.7 at the end of the test

Kinetic of test substance (in %):
= 61.13 after 3 day(s)
= 74.35 after 7 day(s)
= 66.09 after 14 day(s)
= 71.94 after 21 day(s)
= 88.88 after 28 day(s)

Kinetic of control substance (in %):
= 67.15 after 3 day(s)
= 80.93 after 28 day(s)
Degradation products: not measured

The 89% degradation indicated here relates to the Theoritical Oxygen Demand (ThOD).

Validity criteria fulfilled:
yes
Remarks:
Oxygen depletion in the inoculum blank did not exceed 1.5 mg dissolved oxygen/litre after 28 days.
Interpretation of results:
readily biodegradable
Conclusions:
Sodium gluconate (CAS 527-07-1) is readily biodegradable with 89% degradation (based on ThOD) after 28 days.
Executive summary:

The biodegradation of the test substance sodium gluconate (CAS 527-07-1) was investigated according to EU Method C.4-E (Closed bottle test) in compliance with GLP.

All in all, 16 test bottles with a test item concentration of 3 mg/L with 4 mL/L inoculum (secondary effluent of a municipal sewage plant) were filled bubble-free and incubated in the dark at 20°C for 28 days. On days 3, 7, 10, 14, 21 and 28, at least duplicate bottles were removed for determination of dissolved oxygen and pH. At the end of the test, dissolved oxygen concentration in all remaining bottles was measured. Reference item bottles containing sodium acetate stock solution (concentration= 4 mg/L) with 0.4 mL/L inoculum were also filled and incubated in the dark at 20°C. A blank was also prepared without any stock solution.

Referring to the test substance and based on the ThOD, 61.13% degradation were reported after 3 days, followed by 74.35% after 7 days, 66.09% after 14 days, 71.94% after 21 days and 88.88% after 28 days. With regard to the reference substance, 67.15% degradation were measured after 3 days and 80.93% after 28 days – both based on the ThOD.

Description of key information

No biodegradation screening test for copper glucoheptonate was available. Therefore, read-across was performed using the source substance sodium gluconate. This approach is justified since biodegradation is not applicable to dissociating metals in aqueous environement. Therefore, only the organic part of copper glucoheptonate, the glucoheptonate moiety undergoes biodegradation. Glucoheptonates and gluconates differ only in one carbon segment (HCOH): glucoheptonate is longer (C7) than gluconate (C6). Thus, biodegradation is expected to be similar for both substances.

Biodegradation of sodium gluconate (CAS 527-07-1) was investigated according to EU Method C.4-E (Closed bottle test) in compliance with GLP (Hydrotox GmbH, 2001; as cited in OECD SIDS, 2004).

Based on the ThOD, 61.13% degradation were reported after 3 days, followed by 74.35% after 7 days, 66.09% after 14 days, 71.94% after 21 days and 88.88% after 28 days.

Key value for chemical safety assessment

Biodegradation in water:
readily biodegradable

Additional information

Two experimental study reports are cited in the OECD SIDS Report (2004) on Gluconic Acid and its Derivatives. Both studies refer to the read-across substance sodium gluconate (CAS 527 -07 -01). Actual data on the target substance is not available for this endpoint. Nevertheless, conclusions drawn on the read-across substance are assignable for the target substance as well.

Referring to the key information, the biodegradation of sodium gluconate (CAS 527-07-1) was investigated according to EU Method C.4-E (Closed bottle test) in compliance with GLP (Hydrotox GmbH, 2001; as cited in OECD SIDS, 2004).

All in all, 16 test bottles with a test item concentration of 3 mg/L with 4 mL/L inoculum (secondary effluent of a municipal sewage plant) were filled bubble-free and incubated in the dark at 20°C for 28 days. On days 3, 7, 10, 14, 21 and 28, at least duplicate bottles were removed for determination of dissolved oxygen and pH. At the end of the test, dissolved oxygen concentration in all remaining bottles was measured. Reference item bottles containing sodium acetate stock solution (concentration= 4 mg/L) with 0.4 mL/L inoculum were also filled and incubated in the dark at 20°C. A blank was also prepared without any stock solution.

Referring to the test substance and based on the ThOD, 61.13% degradation was reported after 3 days, followed by 74.35% after 7 days, 66.09% after 14 days, 71.94% after 21 days and 88.88% after 28 days. With regard to the reference substance, 67.15% degradation were measured after 3 days and 80.93% after 28 days – both based on the ThOD.

With regard to the supporting information, the biodegradation of sodium gluconate (CAS 527-07-1) was investigated according to DIN EN ISO 11734 in compliance with GLP (Hydrotox GmbH, 2001; as cited in OECD SIDS, 2004).

Washed digested sludge containing very low amounts of inorganic carbon (IC) was diluted to 1-3 g/L total solids concentration and incubated in the absence of oxygen at 35 +/-2°C in sealed vessels with the test item (303 mg/L) at a concentration of 20-200 mg/L total organic carbon (TOC) for 35 days. As reference substance, sodium benzoate (0.069 g/400 mL) has been used. The percentage biodegradation is calculated from the total carbon transformed to biogas and DIC and the measured or calculated amount of carbon added as test item.

Referring to the test substance, 8% degradation has been determined after 1 day, followed by 51% after 8 days, 57% after 15 days, 61% after 22 days and 100% after 35 days. With regard to the reference substance, 6% degradation was determined after 8 days and 100% after 35 days.