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ENVIRONMENTAL EXPOSURE ASSESSMENT<br />

The remarks in the section on soil biodegradation regarding use of half-lives derived in surface<br />

water simulation tests may also apply <strong>for</strong> sediments.<br />

2.3.6.6 Overall rate constant <strong>for</strong> degradation in surface water<br />

In surface water, the substance may be trans<strong>for</strong>med through photolysis, hydrolysis, <strong>and</strong><br />

biodegradation. For calculation of the PECregional, the rate constants <strong>for</strong> these processes can be<br />

summed into one, overall degradation rate constant. It should be noted that different types of<br />

degradation (primary <strong>and</strong> ultimate) are added. This is done <strong>for</strong> modelling purposes only. It<br />

should also be noted that measurements on one degradation process might in fact already include<br />

the effects of other processes. For example, hydrolysis can occur under the conditions of a<br />

biodegradation test or a test of photodegradation, <strong>and</strong> so may already be comprised by the<br />

measured rate from these tests. In order to add the rates of different processes, it should be<br />

determined that the processes occur in parallel <strong>and</strong> that their effects are not already included in<br />

the rates <strong>for</strong> other processes. If exclusion of hydrolysis from the other degradation rates cannot<br />

be confirmed its rate constant should be set to zero. The equation below relates to primary<br />

degradation. If the primary degradation is not the rate-limiting step in the total degradation<br />

sequence <strong>and</strong> degradation products accumulate, then also the degradation product(s) <strong>for</strong>med in<br />

the particular process (e.g. hydrolysis) should be assessed. If this cannot be done or is not<br />

practical, the rate constant <strong>for</strong> the process should be set to zero.<br />

Explanation of symbols<br />

kdegwater = khydrwater + kphotowater + kbiowater (31)<br />

khydrwater first order rate constant <strong>for</strong> hydrolysis in surface water [d -1 ] eq. (26)<br />

kphotowater first order rate constant <strong>for</strong> photolysis in surface water [d -1 ] eq. (27)<br />

kbiowater first order rate constant <strong>for</strong> biodegradation in surface water [d -1 ] Table 7<br />

kdegwater total first order rate constant <strong>for</strong> degradation in surface water [d -1 ]<br />

2.3.7 Elimination processes prior to the release to the environment<br />

2.3.7.1 Wastewater treatment<br />

In this section, the following parameters are derived:<br />

• emission from a sewage treatmentplant to air;<br />

• concentration in sewage sludge;<br />

• concentration in effluent of a sewage treatment plant;<br />

• PEC <strong>for</strong> microorganisms in a sewage treatment plant.<br />

Elimination refers to the reduction in the concentration of substances in gaseous or aqueous<br />

discharges prior to their release to the environment. Elimination from the water phase may occur<br />

by physical as well as chemical or biochemical processes. In a sewage treatment plant (STP),<br />

one of the main physical processes is settling of suspended matter which will also remove<br />

adsorbed material. Physical processes do not degrade a substance but transfer it from one phase<br />

to another e.g. from liquid to solid. In the case of volatile substances, the aeration process will<br />

57

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