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1.
Biofouling ; 36(3): 276-291, 2020 03.
Article in English | MEDLINE | ID: mdl-32338044

ABSTRACT

Metal release rates were measured from four different copper alloy-based materials used by the aquaculture industry: copper sheet machined into a diamond mesh, copper alloy mesh (CAM), silicon bronze welded wire mesh, and copper sheeting, and compared with conventional nylon aquaculture net treated with a cuprous oxide antifouling (AF) coating. Release rates were measured in situ in San Diego Bay using a Navy-developed Dome enclosure system at nine different time points over one year. As expected, copper was the predominant metal released, followed by zinc and nickel, which were fractional components of the materials tested. Release rates followed a temporal trend similar to those observed with copper AF coatings applied to vessel hulls: an initial spike in copper release was followed by a decline to an asymptotic low. Leachate toxicity was consistent with prior studies and was directly related to the metal concentrations, indicating the alloys tested had no additional toxicity above pure metals.


Subject(s)
Alloys/analysis , Copper/analysis , Environmental Monitoring/methods , Water Pollutants, Chemical/analysis , Alloys/chemistry , Bays/chemistry , California , Nickel/analysis , Seawater/chemistry , Zinc/analysis
2.
Biofouling ; 30(1): 51-68, 2014 Jan.
Article in English | MEDLINE | ID: mdl-24199998

ABSTRACT

Copper-based epoxy and ablative antifouling painted panels were exposed in natural seawater to evaluate environmental loading parameters. In situ loading factors including initial exposure, passive leaching, and surface refreshment were measured utilizing two protocols developed by the US Navy: the dome method and the in-water hull cleaning sampling method. Cleaning techniques investigated included a soft-pile carpet and a medium duty 3M(™) pad for fouling removal. Results show that the passive leach rates of copper peaked three days after both initial deployment and cleaning events (CEs), followed by a rapid decrease over about 15 days and a slow approach to asymptotic levels on approximately day 30. Additionally, copper was more bioavailable during a CE in comparison to the passive leaching that immediately followed. A paint life cycle model quantifying annual copper loading estimates for each paint and cleaning method based on a three-year cycle of painting, episodic cleaning, and passive leaching is presented.


Subject(s)
Biofouling/prevention & control , Copper/chemistry , Paint/toxicity , Ships , Biological Availability , Copper/toxicity , Surface Properties , Water Quality
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