5.1 Screening for persistency, bioaccumulation and toxicity
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Statutory Documents - IMO Publications and Documents - Resolutions - Marine Environment Protection Committee - Resolution MEPC.169(57) - Procedure for Approval of Ballast Water Management Systems that make use of Active Substances (G9) - (Adopted on 4 April 2008) - Annex - Procedure for Approval of Ballast Water Management Systems that make use of Active Substances (G9) - 5 Risk Characterization - 5.1 Screening for persistency, bioaccumulation and toxicity

5.1 Screening for persistency, bioaccumulation and toxicity

  5.1.1 An assessment on the intrinsic properties of the Active Substance and/or Preparation such as persistency, bioaccumulation and toxicity should be conducted (see Table 1 in section 6).

  • .1 Persistence tests:

    Persistence should preferably be assessed in simulation test systems that determine the half-life under relevant conditions. Biodegradation screening tests may be used to show that the substances are readily biodegradable. The determination of the half-life should include assessment of relevant chemicals.

  • .2 Bioaccumulation tests:

    The assessment of the (potential for) bioaccumulation should use measured bioconcentration factors in marine (or freshwater) organisms. Where these tests are not applicable, or if logPow <3, Bio Concentration Factor (BCF) values may be estimated using (Quantitative) Structure-Activity Relationship ((Q)SAR) models.

  • .3 Toxicity tests:

    Acute and/or chronic ecotoxicity data, ideally covering the sensitive life stages, should in principle be used for the assessment of the toxicity criterion.


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