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However, these programs used different criteria for categorization.
To serve as the basis for discussions in the rest of the paper, the criteria for categorization are summarized in Table 1.
The use of toxicity data from semi-field and ecosystem-level (cosm) studies is not mentioned in the criteria for categorization.
The criteria for categorization of PPPs as bioaccumulative [10] are principally focused on aquatic systems where pesticides are not routinely applied.
Table 1 Criteria for categorization of compounds as POPs and LRT substances under the SC and UNECE Persistent (P) Bioaccumulative (B) Toxic (T) Potential for long-range transport (LRT) Water: DT501 > 2 months BCF or BAF >5,000 or Log KOW >5 No specific criteria other than 'significant adverse human health and/or environmental effects' (in Article 8, 7 (a)) Air: DT50 > 2 days.
Criteria for categorization are somewhat arbitrary, which is consistent with observations for other publications [ 11].
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Similarly, the criterion for categorization of PPPs as toxic [10] is principally based on aquatic data and lacks appropriate triggers for categorization of toxicity to terrestrial organisms.
After several meetings and discussions among the project team members, the main function of listening text (or activity) has been chosen as the criterion for categorization.
The T criterion for categorization of PBT provides a toxicity threshold but does not indicate a specific kind of organism, although the use of the plural 'organisms' suggests that data from more than one species are to be considered and that it refers to the three trophic levels assumed to be representative of aquatic systems in traditional risk assessment procedures.
The criteria values for categorization were determined from the proposed systems, which could maintain a reactor in a safe state by removing the decay heat for the SBO coping time of 8 h.
There is inconsistency in the criteria used for categorization of various substances under regulations in the EU.
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