4.1 This test method is designed to provide a laboratory procedure to quantify and characterize changes in the release rate of organic biocide from antifouling coatings that occur during a period of immersion under specified laboratory conditions of constant temperature, pH, salinity, and hydrodynamics. Quantitative measurement of biocide release rate is necessary to help in selection of materials, providing quality control, and understanding the performance mechanism.
4.2 Results from this test method establish a pattern of biocide release from an antifouling coating over a minimum of 45 days exposure under controlled laboratory conditions. Biocide release rates of antifouling paints in-service vary over the life of the coating system depending on the formulation and on the physical and chemical properties of the environment. Factors such as differences in berthing locations, operating schedules, length of service, condition of paint film surface, temperature, pH, and salinity influence the actual release rate under environmental conditions. Results obtained using this test method do not reflect actual biocide release rates that will occur in service, but provide comparisons of the release rate characteristics of different antifouling formulations in substitute ocean water under the prescribed laboratory conditions.
4.3 By comparison with published copper and organotin release rate data4,5 obtained either by direct measurements from ship hulls or release rate measurements from harbor exposed panels, all data indicate that the results of this generic rotating-cylinder test method significantly overestimate the release rate of biocide when compared to release rates under in-service conditions. For example, published results demonstrate that this generic test method produces higher measurements of copper and organotin release rates than from direct in situ measurements for the same coating on in-service ship hulls and harbor-exposed panels. The difference between the results of this test method and the panel and ship studies was up to a factor of about 30 based on copper release rate data for several commercial antifouling coatings.4, 6 No direct release rate data from ship hulls or harbor-exposed panels have been generated to-date for the biocides covered by this method. However, the expectation is that the results of this test method, when compared with the direct measurements from ship hulls and harbor-exposed panels, could follow the same trend. Realistic estimates of the biocide release from a ship’s hull under in-service conditions can only be obtained from this test method where the difference between the results obtained by this test method and the release rate of an antifouling coating in service is taken into account.
4.4 Where the results of this test method are used in the process of generating environmental risk assessments, for environmental loading estimates, or for regulatory purposes, it is most strongly recommended that the relationship between laboratory release rates and actual environment inputs is taken into account to allow a more accurate approximation of the biocide release rate from antifouling coatings under real-life conditions. This can be accomplished through the application of appropriate correction factors.
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术语“非活性容器”系指容器,特别是与其水接触表面,不会被水造成任何改变,如与容器有关的溶出物带入水中,或由水造成的化学反应或腐蚀。透析用水中不含添加的抗菌物质,不得用于注射。其质量要求有水电导率、总有机碳(或易氧化物)、微生物限度和细菌内毒素检查。水电导率检查和总有机碳检查要求与纯化水和注射用水的要求一致。然而,有机成分的测定可用易氧化物检查代替总有机碳检查。...
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