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Recently, copper alloys have become important netting materials in aquaculture (the farming of aquatic organisms including fish farming). Various other materials including nylon, polyester, polypropylene, polyethylene, plastic-coated welded wire, rubber, patented rope products (Spectra®, Thorn-D®, Dyneema®), and galvanized steel are also used for netting in aquaculture fish enclosures around the world.[1][2][3][4][5] All of these materials are selected for a variety of reasons, including design feasibility, material strength, cost, and corrosion resistance.

What sets copper alloys apart from the other materials is that copper alloys are antimicrobial, that is, they destroy bacteria, viruses, fungi, algae, and other microbes. (For information about the antimicrobial properties of copper and its alloys, see Antimicrobial properties of copper and Antimicrobial copper alloy touch surfaces).

In the marine environment, the antimicrobial/algaecidal properties of copper alloys prevent biofouling, which can briefly be described as the undesirable accumulation, adhesion, and growth of microorganisms, plants, algae, tubeworms, barnacles, mollusks, and other organisms on man-made marine structures.[6] By inhibiting microbial growth, copper alloy aquaculture cages avoid the need for costly net changes that are necessary with other materials. The resistance of organism growth on copper alloy nets also provides a cleaner and healthier environment for farmed fish to grow and thrive.

In addition to their antifouling benefits, copper alloys have strong structural and corrosion-resistant properties in marine environments.

It is the combination of all of these properties – antifouling, high strength, and corrosion resistance – that has made copper alloys a desirable material for such marine applications as condenser tubing, water intake screens, ship hulls, offshore structure, and sheathing. In the past 25 years or so, the benefits of copper alloys have caught the attention of the marine aquaculture industry. The industry is now actively deploying copper alloy netting and structural materials in commercial large-scale fish farming operations around the world.

Importance of aquaculture in feeding people around the world[edit]

See also: Aquaculture and Fish farming

Much has been written about the degradation and depletion of natural fish stocks in rivers, estuaries, and the oceans (see also overfishing).[7][8] Because industrial fishing has become extremely efficient, ocean stocks of large fish, such as tuna, cod, and halibut have declined by 90% in the past 50 years.[9][10][11]

Aquaculture, an industry that has emerged only in recent decades, has become one of the fastest growing sectors of the world food economy.[2] Aquaculture already supplies more than half of the world’s demand for fish.[12] This percentage is predicted to increase dramatically over the next few decades.

The problem of biofouling in aquaculture[edit]

Biofouling is one of the most important problems in aquaculture.[13] Biofouling occurs on non-copper materials in the marine environment, including fish cage surfaces and nettings.[2] For example, it was noted that the open area of a mesh immersed for only seven days in a Tasmanian aquaculture operation decreased by 37% as a result of biofouling.[14]

The biofouling process begins when algae spores, marine invertebrate larvae, and other organic material adhere to surfaces submerged in marine environments (e.g., fish nets in aquaculture). Bacteria then encourage the attachment of secondary unwanted colonizers.[2][15]

Biofouling has strong negative impacts on aquaculture operations. Water flow, oxygen, and nutrients are inhibited due to clogged nets in fish pens and cages.[16][17] The end result is often diseased fish from infections, such as netpen liver disease,[18] amoebic gill disease,[19] parasites,[20][21] and, in the case of shellfish, poisoning by phytoplankton.[22] Other negative impacts include increased fish deaths, decreased fish growth rates, premature fish harvesting, reduced fish product values and profitability, and an adversely impacted environment near fish farms.[2][23][24]

Biofouling adds enormous weight to submerged fish netting. Two hundredfold increases in weight have been reported.[25][26] This translates, for example, to two thousand pounds of unwanted organisms adhered to what was once a clean 10-pound fish net. In South Australia, biofouling weighing 6.5 tonnes (approximately 13,000 pounds) was observed on a fish net.[27] This extra burden often results in net breakage and additional maintenance costs.

To combat parasites from biofouling, pesticides such as cypermethrin, azamethiphos, and emamectin benzoate may be administered, but these have been found to have detrimental environmental effects, for example, in lobster operations.[28][29][30][31][32]

To treat diseases in fish raised in biofouled nets, fish stocks are administered antibiotics. The antibiotics can have unwanted long-term health effects on consumers and on coastal environments near aquaculture operations.[33] To combat biofouling, operators often implement costly maintenance measures, such as frequent net changing, cleaning/removal of unwanted organisms from nets, net repairs, and chemical treatment including antimicrobial coatings on nylon nets.[19][34][35][36] The cost of antifouling a single salmon net can be several thousand British pounds.[2] In some sectors of the European aquaculture industry, cleaning biofouled fish and shellfish cages can cost 5-20% of its market value. Heavy fouling can reduce the saleable product in nets by 60-90%.[23]

Antifouling paints are often used on nylon nets because the process is more economical than manual cleaning.[37] When nylon nets are coated with antifouling paints, the coatings repel biofouling for a period of time, usually between several weeks to several months. However, the nets eventually succumb to biofouling. Antifouling paints containing cuprous oxide algaecide/biocide are the paint technology used almost exclusively in the fish farming industry today. The treatments usually flake off within a few weeks to six to eight months.[2][38]

Biofouled nets are replaced weekly or after several months of service, depending on environmental conditions, in a complicated, costly, and labor-intensive operation that involves divers and specialized personnel. During this process, live fish in nets must be transferred to clean cages, which causes undue stress and asphyxiation that results in some loss of fish.[39] Biofouled nets that can be reused are washed on land via manual brushing and scrubbing or high-pressure water hosing. They are then dried and re-impregnated with antifouling liquids.[26][38][40][41]

A line of net cleaners is available for in-situ washings where permitted.[42] But, even where not permitted by environmental, fisheries, maritime, and sanitary authorities, should the lack of oxygen in submerged cages create an emergency condition that endangers the health of fish, divers may be deployed with special in situ cleaning machinery to scrub biofouled nets.[38]

The aquaculture industry is addressing the negative environmental impacts from its operations (see aquaculture issues). As the industry evolves, a cleaner, more sustainable aquaculture industry is expected to emerge, one that may increasingly rely on materials with anti-fouling, anti-corrosive, and strong structural properties, such as copper alloys.

Antifouling properties of copper alloys in the marine environment[edit]

See also: Antimicrobial properties of copper and Antimicrobial copper alloy touch surfaces

In the aquaculture industry, sound animal husbandry translates to keeping fish clean, well fed, healthy, and not overcrowded.[43] One solution to keeping farmed fish healthy is to contain them in antifouling copper alloy nets and structures.[44]

Researchers have attributed copper’s resistance to biofoul, even in temperate waters, to two possible mechanisms: 1) a retarding sequence of colonization through release of antimicrobial copper ions, thereby preventing the attachment of microbial layers to marine surfaces;[45] and, 2) separating layers that contain corrosive products and the spores of juveniles or macro-encrusting organisms.[46]

The most important requirement for optimum biofouling resistance is that the copper alloys should be freely exposed or electrically insulated from less noble alloys and from cathodic protection. Galvanic coupling to less noble alloys and cathodic protection prevent copper ion releases from surface films and therefore reduce biofouling resistance.[47]

As temperatures increase and water velocities decrease in marine waters, biofouling rates dramatically rise. However, copper’s resistance to biofouling is observed even in temperate waters. Studies in Herrdura Bay, Chile, where biofouling conditions are extreme, demonstrated that a copper alloy (90% copper, 10% nickel) avoided macro-encrusting organisms.[46]

Corrosion behavior of copper alloys used in marine aquaculture[edit]

Copper alloys used in sea water service have low general corrosion rates but also have a high resistance to many localized forms of corrosion. For a technical discussion regarding various types of corrosion, application considerations (e.g., depth of installations, effect of polluted waters, sea conditions), and the corrosion characteristics of several copper alloys used in aquaculture netting (i.e., copper-nickel, copper-zinc, and copper-silicon[48]).

Environmental performance of copper alloy mesh in marine fish farming[edit]

Many complicated factors influence the environmental performance of copper alloys in aquaculture operations. A technical description of antibiofouling mechanisms, fish health and welfare, fish losses due to escapes and predator attacks, and reduced life cycle environmental impacts is summarized in this reference.[49]

Types of copper alloys used in aquaculture[edit]

Copper-zinc brass alloys are being deployed today in commercial-scale aquaculture operations in Asia and South America. Extensive research, including demonstrations and trials, are currently being implemented on two other copper alloys: copper-nickel and copper-silicon. Each of these alloy types has an inherent ability to reduce biofouling, cage waste, disease, and the need for antibiotics while simultaneously maintaining water circulation and oxygen requirements. Other types of copper alloys are also being considered for research and development in aquaculture operations.

The University of New Hampshire is in the midst of conducting experiments under the auspices of the International Copper Association (ICA)[50] to evaluate the structural, hydrodynamic, and antifouling response of copper alloy nets. Factors to be determined from these experiments, such as drag, cage dynamic loads, material loss, and biological growth – well documented for nylon netting but not fully understood for copper-nickel alloy nets – will help to design fish cage enclosures made from these alloys. The East China Sea Fisheries Research Institute, in Shanghai, China, is also conducting experimental investigations on copper alloys for ICA.

Copper-zinc alloys[edit]

The Mitsubishi-Shindoh Co., Ltd., has developed a proprietary copper-zinc brass alloy, UR30™, specifically designed for aquaculture operations. The alloy, which is composed of 64% copper, 35.1% zinc, 0.6% tin, and 0.3% nickel, resists mechanical abrasion when formed into wires and fabricated into chain link, woven, or other types of flexible mesh. Corrosion rates depend on the depth of submersion and seawater conditions. The average reported corrosion rate reported for the alloy is <5 μm/yr based on 2- and 5-year exposure trials in seawater.[51]

The Ashimori Industry Company, Ltd.,[52] has installed approximately 300 flexible cages with woven chain link UR30™ meshes in Japan to raise Seriola (i.e., yellowtail, amberjack, kingfish, hamachi). The company has installed another twenty-eight UR30™ cages to raise Atlantic salmon at the Van Diemen Aquaculture operations in Tasmania, Australia. In Chile, EcoSea Farming S.A. expects to have installed a total of approximately forty woven chain link UR30™ mesh cages by the end of 2010 to raise trout and Atlantic salmon.[51] And in Panama and the USA, demonstrations and trials are underway using flexible cages with woven chain link UR30™.

To date, in over 10 years of aquaculture experience, chain link mesh fabricated by UR30™ alloys have not suffered from dezincification, stress corrosion cracking, or erosion corrosion.

Additional information about UR30™ can be found at the following Websites: chemical composition of UR30™[53]; physical properties of UR30™[54]; diameters available for UR30™[55]; corrosion resistance of UR30™[56]; and mechanical properties of UR30™[57].

Alternative copper-zinc alloys for aquaculture are being developed by other companies but have not yet been deployed in commercial operations.

Copper-nickel alloys[edit]

Copper-nickel alloys were developed specifically for seawater applications over five decades ago. Today, these alloys are being investigated for their potential use in aquaculture.

Copper-nickel alloys for marine applications are usually comprised of 90% copper, 10% nickel, plus small amounts of manganese and iron to enhance corrosion resistance. The seawater corrosion resistance of copper-nickel alloys results in a thin, adherent, protective surface film which forms naturally and quickly on the metal upon exposure to clean seawater.[58]

The rate of corrosion protective formation is temperature dependent. For example, at 27°C (i.e., a common inlet temperature in the Middle East), rapid film formation and good corrosion protection can be expected within a few hours. At 16°C, it could take 2–3 months for the protection to mature. But once a good surface film forms, corrosion rates decrease, normally to 0.02-0.002 mm/yr, as protective layers develop over a period of years.[59] These alloys have good resistance to chloride pitting and crevice corrosion and are not susceptible to chloride stress corrosion.

Copper-silicon alloys[edit]

Copper-silicon has a long history of use as screws, nuts, bolts, washers, pins, lag bolts, and staples in wooden sailing vessels in marine environments. The alloys are often composed of 96% copper, 3% silicon, and 1% manganese. The inclusion of silicon strengthens the metal.

As with the copper-nickel alloys, corrosion resistance of copper-silicon is due to protective films that form on the surface over a period of time. General corrosion rates of 0.025-0.050mm have been observed in quiet waters. This rate decreases towards the lower end of the range over long-term exposures (e.g., 400–600 days). There is generally no pitting with the silicon-bronzes and, if pitting does occur, the pits are small. Also there is good resistance to erosion corrosion up to moderate flow rates. Because copper-silicon is weldable, rigid cages can be constructed with this material. Also, because welded copper-silicon mesh is lighter than copper-zinc chain link, aquaculture enclosures made with copper-silicon may be lighter in weight and therefore a potentially less expensive alternative.

Luvata Appleton, LLC, is researching and developing a line of copper-silicon alloy woven meshes and welded meshes under the patent-pending trade name Seawire.™[60]. Copper-silicon alloy meshes have been developed by the firm to raise various marine organisms in test trials that are now in various stages of evaluation. These include raising cobia in Panama, lobsters in Maine, and crabs in the Chesapeake Bay. The company is working with various universities to study its material, including the University of Arizona to study shrimp, the University of New Hampshire to study cod, and Oregon State University to study oysters. Results will be provided when the studies are concluded.

References[edit]

  1. ^ Offshore Aquaculture in the United States: Economic considerations, implications, and opportunities, U.S. Department of Commerce, National Oceanic & Atmospheric Administration, July 2008, p. 53
  2. ^ a b c d e f g Braithwaite, RA; McEvoy, LA (2005). "Marine biofouling on fish farms and its remediation". Advances in marine biology. 47: 215–52. doi:10.1016/S0065-2881(04)47003-5. PMID 15596168.
  3. ^ "Commercial and research fish farming and aquaculture netting and supplies". Sterlingnets.com. Retrieved 2010-06-16.
  4. ^ "Aquaculture Netting by Industrial Netting". Industrialnetting.com. Retrieved 2010-06-16.
  5. ^ Southern Regional Aquaculture Center at http://aquanic.org/publicat/usda_rac/efs/srac/162fs.pdf
  6. ^ Marine Fouling and its Prevention, Wood Hole Oceanographic Institution, 1952, United States Naval Institute, Annapolis, Maryland, USA
  7. ^ Myers, Ransom A.; Worm, Boris (2003). "Rapid worldwide depletion of predatory fish communities". Nature. 423 (6937): 280. doi:10.1038/nature01610. PMID 12748640.
  8. ^ The State of World Fisheries and Aquaculture (SOFIA), Biennial Report, 2005, as summarized in Food and Agriculture Organization of the United Nations
  9. ^ The Next Seafood Frontier: The Ocean, April 28, 2009, references article by Myers in Nature
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  12. ^ Half Of Fish Consumed Globally Is Now Raised On Farms, Study Finds Science Daily, September 8, 2009
  13. ^ Design Guide: Copper Alloy Mesh in Marine Aquaculture, International Copper Research Association Inc. (INCRA), 1984
  14. ^ Hodson, Stephen; Burke, Christopher; Lewis, Thomas (1995). "In situ quantification of fish-cage fouling by underwater photography and image analysis". Biofouling. 9: 145. doi:10.1080/08927019509378298.
  15. ^ Bakus, Gerald J.; Targett, Nancy M.; Schulte, Bruce (1986). "Chemical ecology of marine organisms: an overview". Journal of Chemical Ecology. 12: 951. doi:10.1007/BF01638991.
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  17. ^ Ahlgren, M.O., (1998), Consumption and assimilation of salmon net pen fouling debris by the red sea cucumber Parastichopus califormicus: Implications for poly-culture, Journal of the World Aquaculture Society, Vol. 29, pp. 133-139
  18. ^ Andersen, RJ; Luu, HA; Chen, DZ; Holmes, CF; Kent, ML; Le Blanc, M; Taylor, FJ; Williams, DE (1993). "Chemical and biological evidence links microcystins to salmon 'netpen liver disease'". Toxicon : official journal of the International Society on Toxinology. 31 (10): 1315–23. PMID 8303725.
  19. ^ a b Nowak, C (2002). "Biofouling as a reservoir of Neoparamoeba pemaquidensis (Page, 1970), the causative agent of amoebic gill disease in Atlantic salmon". Aquaculture. 210: 49. doi:10.1016/S0044-8486(01)00858-4.
  20. ^ González, L (1998). "The life cycle of Hysterothylacium aduncum (Nematoda: Anisakidae) in Chilean marine farms". Aquaculture. 162: 173. doi:10.1016/S0044-8486(97)00303-7.
  21. ^ Huse, I; Bjordal, A; Ferno, A; Furevik, D (1990). "The effect of shading in pen rearing of Atlantic salmon (Salmo salar)". Aquacultural Engineering. 9: 235. doi:10.1016/0144-8609(90)90018-U.
  22. ^ Ross, K.A. et. al., (2002), Fouling in scallop cultivation: Help or hinderance? Journal of Shellfish Research, Vol. 21, pp. 539-547
  23. ^ a b Collective research on Aquaculture Biofouling
  24. ^ Folke, C.; et al. (1997). "Salmon farming in context: Response to Black et al". Journal of Environmental Management. 50: 95–103. doi:10.1006/jema.1996.0097. {{cite journal}}: Explicit use of et al. in: |author= (help)
  25. ^ Milne, P.H., (1970), Fish Farming: A guide to the design and construction of net enclosures, Marine Research, Vol. 1, pp. 1-31 ISBN 0114904634
  26. ^ a b Beveridge, M. (2004), Cage Aquaculture. The University Press, Cambridge ISBN 1405108428
  27. ^ Cronin, E. R.; Cheshire, A. C.; Clarke, S. M.; Melville, A. J. (1999). "An investigation into the composition, biomass and oxygen budget of the fouling community on a tuna aquaculture farm". Biofouling. 13: 279. doi:10.1080/08927019909378386.
  28. ^ Burridge, L; Haya, K; Zitko, V; Waddy, S (1999). "The Lethality of Salmosan (Azamethiphos) to American Lobster (Homarus americanus) Larvae, Postlarvae, and Adults". Ecotoxicology and Environmental Safety. 43 (2): 165. doi:10.1006/eesa.1999.1771. PMID 10375419.
  29. ^ Burridge, L (2000). "The lethality of the cypermethrin formulation Excis® to larval and post-larval stages of the American lobster (Homarus americanus)". Aquaculture. 182: 37. doi:10.1016/S0044-8486(99)00252-5.
  30. ^ Burridge, L (2000). "The lethality of anti-sea lice formulations Salmosan® (Azamethiphos) and Excis® (Cypermethrin) to stage IV and adult lobsters (Homarus americanus) during repeated short-term exposures". Aquaculture. 182: 27. doi:10.1016/S0044-8486(99)00251-3.
  31. ^ Ernst, W; Jackman, P; Doe, K; Page, F; Julien, G; MacKay, K; Sutherland, T (2001). "Dispersion and Toxicity to Non-target Aquatic Organisms of Pesticides Used to Treat Sea Lice on Salmon in Net Pen Enclosures". Marine Pollution Bulletin. 42: 432. doi:10.1016/S0025-326X(00)00177-6.
  32. ^ Waddy, S.L.; et al. (2002). "Emamectin benzoate induces molting in American lobster Homarus americanus" (PDF). Canadian Journal of Fisheries and Aquatic Sciences. 59: 1096–1099. doi:10.1139/F02-106. {{cite journal}}: Explicit use of et al. in: |author= (help)
  33. ^ The next seafood frontier: The ocean, April 28, 2009, references article by Myers in Nature;
  34. ^ Hodson, S (1997). "Biofouling of fish-cage netting: efficacy and problems of in situ cleaning". Aquaculture. 152: 77. doi:10.1016/S0044-8486(97)00007-0.
  35. ^ Li, S. (1994), Fish culture in cages and pens: Freshwater Fish Culture in China: Principles and Practice, pp. 305-346, Elsevier, Amsterdam ISBN 0444888829
  36. ^ Beveridge, M. (1996), Cage Aquaculture, The University Press, Cambridge
  37. ^ Short, J; Thrower, F (1987). "Toxicity of tri-n-butyl-tin to chinook salmon, Oncorhynchus tshawytscha, adapted to seawater". Aquaculture. 61: 193. doi:10.1016/0044-8486(87)90148-7.
  38. ^ a b c Alberto, Jose and Disselkoen, Ochoa (2009), Floating device to clean nets, Patent application 12/455,150, Publication US 2010/0006036 A1, Filing date May 27; and National Chilean Patent Application No. 1565-2008 filed on May 29, 2008
  39. ^ Paclibare et al., (1994), Clearing of the kidney-disease bacterium Renibacterium salmoninarum from seawater by the blue mussel Mytilus edulis, and the status of the mussel as a reservoir of the bacterium, Diseases of Aquatic Organisms, Vol. 18, pp. 129–133
  40. ^ Enright, C., (1993), Control of fouling in bivalve aquaculture, World Aquaculture, Vol. 24, pp. 44–46
  41. ^ Lee et al., (1985), Observations on the use of antifouling paint in netcage fish farming in Singapore, Singapore Journal of Primary Industries, Vol. 13, pp. 1-12
  42. ^ Idema Net Cleaning Systems
  43. ^ Offshore Aquaculture in the United States: Economic Considerations, Implications, & Opportunities, U.S. Department of Commerce, National Oceanic & Atmospheric Administration, July 2008
  44. ^ "Copper Nickel : References". Copper.org. Retrieved 2010-06-16.
  45. ^ Sutherland, I.W., 1983, Microbial exopolysaccarides: Their role in microbial adhesion in aqueous systems, Critical Reviews in Microbiology, Vol. 10, pp.173-201
  46. ^ a b Edding, Mario E., Flores, Hector, and Miranda, Claudio, (1995), Experimental Usage of Copper-Nickel Alloy Mesh in Mariculture. Part 1: Feasibility of usage in a temperate zone; Part 2: Demonstration of usage in a cold zone; Final report to the International Copper Association Ltd.
  47. ^ Powell, Carol and Stillman, Hal (2009), Corrosion behavior of copper alloys used in marine aquaculture
  48. ^ Corrosion Behaviour of Copper Alloys used in Marine Aquaculture
  49. ^ Environmental Performance of Copper Alloy Mesh in Marine Fish Farming: The Case for Using Solid Copper Alloy Mesh
  50. ^ "Welcome to CopperInfo - Your Worldwide Copper Information Source". Copperinfo.com. Retrieved 2010-06-16.
  51. ^ a b EcoSea Farming S.A.
  52. ^ "Ashimori Industry Co.,Ltd". Ashimori.co.jp. Retrieved 2010-06-16.
  53. ^ Saburo Kito. "UR_Chemicals". Mitsubishi-shindoh.com. Retrieved 2010-06-16.
  54. ^ Saburo Kito. "UR_Physicals". Mitsubishi-shindoh.com. Retrieved 2010-06-16.
  55. ^ Saburo Kito. "UR_Sizes". Mitsubishi-shindoh.com. Retrieved 2010-06-16.
  56. ^ Saburo Kito. "UR_Corrosion". Mitsubishi-shindoh.com. Retrieved 2010-06-16.
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  58. ^ "Copper Nickels : Seawater Corrosion Resistance and Antifouling". Copper.org. 2005-12-15. Retrieved 2010-06-16.
  59. ^ The Application of Copper-Nickel Alloys in Marine Systems, CDA Inc. Seminar-Technical Report 7044-1919, 1996
  60. ^ www.luvata.com; Seawire™ is a trademark of Luvata Appleton, LLC. The company intends to market a wide range of alloys in addition to copper-silicon under this trademark

Further reading[edit]

  • Design Guide: Copper Alloy Mesh in Marine Aquaculture, 1984, International Copper Research Association (INCRA) 704/5.
  • Metal Corrosion in Boats, Nigel Warren and Adlard Coles, Nautical, 1998.
  • Galvanic Corrosion: A Practical Guide for Engineers, R. Francis, 2001, NACE Press.
  • Marine Corrosion Causes and Prevention, F. LaQue, John Wiley and Sons, 1975.
  • The Selection of Materials for Seawater cooling Systems: A Practical Guide for Engineers, R. Francis, 2006, NACE Press.
  • Guidelines for the Use of Copper Alloys in Seawater, A. Tuthill. 1987. CDA/ Nickel Institute Publication.
  • The Brasses: Properties and Applications, CDA UK Publication 117.
  • Copper in the Ocean Environment, Neal Blossom, American Chemet Corporation.
  • ICA Project 438: Experimental usage of copper nickel alloy mesh in aquaculture, Mario E. Edding, Hector Flores, Claudio Miranda, Universidad Catholica del Norte, July 1995

External links[edit]

Category:Copper

Category:Aquaculture

Category:Aquaculture engineering

Category:Fish farming

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