3.5 Data on environmental fate and effect under aerobic and anaerobic conditions (Procedure (G9), paragraph 4.2.1.3)
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Statutory Documents - IMO Publications and Documents - Circulars - Ballast Water Management - BWM.2/Circular.37 – International Convention for the Control and Management of Ships' Ballast Water and Sediments, 2004 – (14 June 2012)... - Annex – Information that should be made available in the Applications for Approval in accordance with Paragraph 8 of the Procedure for Approval of BWM Systems that make use of Active Substances (G9) (The Non-Confidential Information to be Submitted to MEPC) - 3 Application Data Set - 3.5 Data on environmental fate and effect under aerobic and anaerobic conditions (Procedure (G9), paragraph 4.2.1.3)

3.5 Data on environmental fate and effect under aerobic and anaerobic conditions (Procedure (G9), paragraph 4.2.1.3)

3.5.2 Modes of degradation (biotic; abiotic)

 Information on the specific degradation rates (biotic and abiotic) at different salinities and temperatures is desirable for the evaluation of the persistence of all substances and can be used for the MAMPEC calculations. Potential environmental, health and safety consequences of observed degradation rates should be discussed as appropriate.

3.5.3 Persistence and identification of the main metabolites in the relevant media (ballast water, marine and fresh waters)

 The results from section 3.5.2 should be discussed here regarding the classification as persistent (PBT-approach) substances. Relevant metabolites should be identified and it should be discussed whether they possess hazardous properties according to the PBT assessment.

3.5.4 Bioaccumulation, partition coefficient, octanol/water partition Coefficient

 To be able to evaluate the MAMPEC calculations the octanol-water partition coefficient Kow is needed. The bioaccumulation already is discussed under 3.3.6 and 3.3.7.

3.5.5 Bioavailability/biomagnification/bioconcentration

 For the evaluation of the potential for bioaccumulation, the log Kow and/or the bioconcentration factors (BCF) data is needed. Calculation of the Kow according to acknowledged standards, e.g. ACD is acceptable. A substance is regarded as (potentially) bioaccumulative if the log Kow is >3 and BCF>2000. If the log Kow is above 3, testing of the bioaccumulation potential should be considered. The BCF, for example, could be calculated with the formulae 74 and 75 of the TGD (see 3.3.5) using the log Kow. Other established methods for deriving the BCF may be used. Where tests are not applicable, or if log Kow <3, BCF values may be estimated using (Quantitative) Structure-Activity Relationship ((Q)SAR) models.

3.5.6 Reaction with organic matter

 If there are reactions with organic matter these should be discussed. It should be described to what extent this issue was investigated, experimentally or by analysis of available literature data.

3.5.7 Potential physical effects on wildlife and benthic habitats

 If there are effects on wildlife and benthic habitats, these should be discussed.

3.5.8 Potential residues in seafood

 If there are potential residues in seafood, these should be discussed taking into account the PBT and mammalian toxicity properties of the substances.

3.5.9 Any known interactive effects

 It should be described to what extent this issue was investigated, experimentally or by analysis of available literature data. If there are identified or suspected interactive effects, these should be discussed.


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