Knowledge (XXG)

Biofouling

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44: 496:, or PDMS, which consists of a non-polar backbone made of repeating units of silicon and oxygen atoms. The non-polarity of PDMS allows for biomolecules to readily adsorb to its surface in order to lower interfacial energy. However, PDMS also has a low modulus of elasticity that allows for the release of fouling organisms at speeds of greater than 20 knots. The dependence of effectiveness on vessel speed prevents use of PDMS on slow-moving ships or those that spend significant amounts of time in port. 438: 700: 33: 192: 269: 692:; and "Brown stuff", which was simply sulfur added to Black stuff. In many of these cases, the purpose of these treatments is ambiguous. There is dispute whether many of these treatments were actual anti-fouling techniques, or whether, when they were used in conjunction with lead and wood sheathing, they were simply intended to combat wood-boring 364:
operational opening of their valves. Consequently, stock affected by biofouling can experience reduced growth, condition and survival, with subsequent negative impacts on farm productivity. Although many methods of removal exist, they often impact the cultured species, sometimes more so than the fouling organisms themselves.
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filters to collect microbes, some pathogens do pass through these filters, collect inside the device and are eventually blown out and infect other patients. Devices used in operating rooms rarely include fans, so as to minimize the chance of transmission. Also, medical equipment, HVAC units, high-end
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Fouling detection relies on the biomass' property of fluorescence. All microorganisms contain natural intracellular fluorophores, which radiate in the UV range when excited. At UV-range wavelengths, such fluorescence arises from three aromatic amino acids—tyrosine, phenylalanine, and tryptophan. The
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Historically, the focus of attention has been the severe impact due to biofouling on the speed of marine vessels. In some instances the hull structure and propulsion systems can become damaged. Over time, the accumulation of biofoulers on hulls increases both the hydrodynamic volume of a vessel and
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drug delivery devices, papermaking and pulp industry machines, underwater instruments, fire protection system piping, and sprinkler system nozzles. In groundwater wells, biofouling buildup can limit recovery flow rates, as is the case in the exterior and interior of ocean-laying pipes where fouling
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when the host surface is another organism and the relationship is not parasitic. Since biofouling can occur almost anywhere water is present, biofouling poses risks to a wide variety of objects such as boat hulls and equipment, medical devices and membranes, as well as to entire industries, such as
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By the mid-twentieth century, copper oxide-based paints could keep a ship out of drydock for as much as 18 months, or as little as 12 in tropical waters. The shorter service life was due to rapid leaching of the toxicant, and chemical conversion into less toxic salts, which accumulated as a crust
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Ultrasonic transducers may be mounted in or around the hull of small to medium-sized boats. Research has shown these systems can help reduce fouling, by initiating bursts of ultrasonic waves through the hull medium to the surrounding water, killing or denaturing the algae and other microorganisms
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of up to 60%. The drag increase has been seen to decrease speeds by up to 10%, which can require up to a 40% increase in fuel to compensate. With fuel typically comprising up to half of marine transport costs, antifouling methods save the shipping industry a considerable amount of money. Further,
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As an alternative to organotin toxins, there has been renewed interest in copper as the active agent in ablative or self polishing paints, with reported service lives up to 5 years; yet also other methods that do not involve coatings. Modern adhesives permit application of copper alloys to steel
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can be used to control biofouling. In less controlled environments, organisms are killed or repelled with coatings using biocides, thermal treatments, or pulses of energy. Nontoxic mechanical strategies that prevent organisms from attaching include choosing a material or coating with a slippery
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of up to 60% The additional drag can decrease speeds up to 10%, which can require up to a 40% increase in fuel to compensate. With fuel typically comprising up to half of marine transport costs, biofouling is estimated to cost the US Navy alone around $ 1 billion per year in increased fuel
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The buildup of biofouling on marine vessels poses a significant problem. In some instances, the hull structure and propulsion systems can be damaged. The accumulation of biofoulers on hulls can increase both the hydrodynamic volume of a vessel and the hydrodynamic friction, leading to increased
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of the impact fouling had on ship speed goes as follows: "when weeds, ooze, and filth stick upon its sides, the stroke of the ship is more obtuse and weak; and the water, coming upon this clammy matter, doth not so easily part from it; and this is the reason why they usually calk their ships."
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Medical devices used in operating rooms, ICUs, isolation rooms, biological analysis labs, and other high-contamination-risk areas have negative pressure (constant exhaust) in the rooms, maintain strict cleaning protocols, require equipment with no fans, and often drape equipment in protective
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Biofouling also impacts aquaculture, increasing production and management costs, while decreasing product value. Fouling communities may compete with shellfish directly for food resources, impede the procurement of food and oxygen by reducing water flow around shellfish, or interfere with the
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The second class of non-toxic antifouling coatings are hydrophilic coatings. They rely on high amounts of hydration in order to increase the energetic penalty of removing water for proteins and microorganisms to attach. The most common examples of these coatings are based on highly hydrated
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One trend of research is the study of the relationship between wettability and anti-fouling effectiveness. Another trend is the study of living organisms as the inspiration for new functional materials. For example, the mechanisms used by marine animals to inhibit biofouling on their skin.
512:. These coatings are also low-friction, but are considered by some to be superior to hydrophobic surfaces because they prevent bacteria attachment, preventing biofilm formation. These coatings are not yet commercially available and are being designed as part of a larger effort by the 2328:
Carman, Michelle L.; Estes, Thomas G.; Feinberg, Adam W.; Schumacher, James F.; Wilkerson, Wade; Wilson, Leslie H.; Callow, Maureen E.; Callow, James A.; Brennan, Anthony B. (January 2006). "Engineered antifouling microtopographies – correlating wettability with cell attachment".
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Shipping companies have historically relied on scheduled biofouler removal to keep such accretions to a manageable level. However, the rate of accretion can vary widely between vessels and operating conditions, so predicting acceptable intervals between cleanings is difficult.
554:(TBT) compounds were used as biocides (and thus anti-fouling agents). TBTs are toxic to both microorganisms and larger aquatic organisms. The international maritime community has phased out the use of organotin-based coatings. Replacing organotin compounds is 573:
that form the beginning of the fouling sequence. The systems cannot work on wooden-hulled boats, or boats with a soft-cored composite material, such as wood or foam. The systems have been loosely based on technology proven to control algae blooms.
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The earliest attestations of attempts to counter fouling, and thus also the earliest attestation of knowledge if it, is the use of pitch and copper plating as anti-fouling solutions that were attributed to ancient seafaring nations, such as the
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usage, maintenance and biofouling control measures. Increased fuel use due to biofouling contributes to adverse environmental effects and is predicted to increase emissions of carbon dioxide and sulfur dioxide between 38 and 72 percent by 2020.
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Biofouling organisms are highly diverse, and extend far beyond the attachment of barnacles and seaweeds. According to some estimates, over 1,700 species comprising over 4,000 organisms are responsible for biofouling. Biofouling is divided into
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Sievers, Michael; Dempster, Tim; Fitridge, Isla; Keough, Michael J. (8 January 2014). "Monitoring biofouling communities could reduce impacts to mussel aquaculture by allowing synchronisation of husbandry techniques with peaks in settlement".
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where it is not wanted on surfaces such as ship and submarine hulls, devices such as water inlets, pipework, grates, ponds, and rivers that cause degradation to the primary purpose of that item. Such accumulation is referred to as
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Taylor, S.; et al. (1994). "trans-2,3-cis-3,4-Dihydroxyproline, a New Naturally Occurring Amino Acid, Is the Sixth Residue in the Tandemly Repeated Consensus Decapeptides of an Adhesive Protein from Mytilus edulis".
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typically involves heating a medical device to 121 Â°C (249 Â°F) for 15–20 minutes. Ultrasonic cleaning, UV light, and chemical wipe-down or immersion can also be used for different types of devices.
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Regimens to periodically use heat to treat exchanger equipment and pipes have been successfully used to remove mussels from power plant cooling systems using water at 105 Â°F (40 Â°C) for 30 minutes.
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hulls without creating galvanic corrosion. However, copper alone is not impervious to diatom and algae fouling. Some studies indicate that copper may also present an unacceptable environmental impact.
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The copper performed well in protecting the hull from invasion by worm, and in preventing the growth of weed, for when in contact with water, the copper produced a poisonous film, composed mainly of
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Yebra, Diego Meseguer; Kiil, Søren; Dam-Johansen, Kim (July 2004). "Antifouling technology—past, present and future steps towards efficient and environmentally friendly antifouling coatings".
585:. Plasma pulse technology is effective against zebra mussels and works by stunning or killing the organisms with microsecond-duration energizing of the water with high-voltage electricity. 1460:
Pit, Josiah H.; Southgate, Paul C. (2003). "Fouling and predation; how do they affect growth and survival of the blacklip pearl oyster, Pinctada margaritifera, during nursery culture?".
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Governments and industry spend more than US$ 5.7 billion annually to prevent and control marine biofouling. Biofouling occurs everywhere but is most significant economically to the
143:—attachment of larger organisms. Due to the distinct chemistry and biology that determine what prevents them from settling, organisms are also classified as hard- or soft-fouling types. 1316:
Babič, Monika; Gunde-Cimerman, Nina; Vargha, Márta; Tischner, Zsófia; Magyar, Donát; Veríssimo, Cristina; Sabino, Raquel; Viegas, Carla; Meyer, Wieland; Brandão, João (13 June 2017).
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in bacteria, viruses, and other microbes. Preventing biofilm formation prevents larger organisms from attaching themselves to the instrument and eventually rendering it inoperable.
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Evans, S.M.; Leksono, T.; McKinnell, P.D. (January 1995). "Tributyltin pollution: A diminishing problem following legislation limiting the use of TBT-based anti-fouling paints".
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Biofouling is also found in almost all circumstances where water-based liquids are in contact with other materials. Industrially important impacts are on the maintenance of
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irradiation is a noncontact, nonchemical solution that can be used across a range of instruments. Radiation in the UVC range prevents biofilm formation by deactivating the
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and silicone coatings are commonly used. These coatings are ecologically inert but have problems with mechanical strength and long-term stability. Specifically, after days
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Gang Cheng; et al. (2 June 2010), "Integrated Antimicrobial and Nonfouling Hydrogels to Inhibit the Growth of Planktonic Bacterial Cells and Keep the Surface Clean",
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when they were found to be very toxic to diverse organisms. TBT in particular has been described as the most toxic pollutant ever deliberately released in the ocean.
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computers, swimming pools, drinking-water systems and other products that utilize liquid lines run the risk of biofouling as biological growth occurs inside them.
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have been used since early times. An Aramaic record dating from 412 BC tells of a ship's bottom being coated with a mixture of arsenic, oil and sulphur. In
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and was referred to as "McIness" hot plastic paint. These treatments had a short service life, were expensive, and relatively ineffective by modern standards.
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Non-toxic anti-sticking coatings prevent attachment of microorganisms thus negating the use of biocides. These coatings are usually based on organic polymers.
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Jiang, S.; Cao, Z. (2010), "Ultralow-Fouling, Functionalizable, and Hydrolyzable Zwitterionic Materials and Their Derivatives for Biological Applications",
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Biocides are chemical substances that kill or deter microorganisms responsible for biofouling. The biocide is typically applied as a paint, i.e. through
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set about coppering the bottoms of the entire fleet and continued to the end of the use of wooden ships. The process was so successful that the term
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Rouhi, A. Maureen (27 April 1998). "The Squeeze On Tributyltins: Former EPA adviser voices doubts over regulations restricting antifouling paints".
227:. By the end of the first week, the rich nutrients and ease of attachment into the biofilm allow secondary colonizers of spores of macroalgae (e.g. 492:(slime) can coat the surfaces, which buries the chemical activity and allows microorganisms to attach. The current standard for these coatings is 837:
A study of the biotoxins used by organisms has revealed several effective compounds, some of which are more powerful than synthetic compounds.
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increased fuel use due to biofouling contributes to adverse environmental effects and is predicted to increase emissions of carbon dioxide and
2410: 2120: 1983: 972: 852:(PEG). Growing chains of PEG on surfaces is challenging. The resolution to this problem may come from understanding the mechanisms by which 43: 208: 343:. Besides interfering with mechanisms, biofouling also occurs on the surfaces of living marine organisms, when it is known as epibiosis. 2533: 2166: 777: 1936:
Sommerville, David C. (September 1986), "Development of a Site Specific Biofouling Control Program for the Diablo Canyon Power Plant",
1271:"Waterborne microorganisms and biofilms related to hospital infections: strategies for prevention and control in healthcare facilities" 2394: 2063: 845:, was found to be over 100 times as potent as TBT, and over 6,000 times more effective in anti-settlement activity against barnacles. 800: 672:
Before the 18th century, various anti-fouling techniques were used, with three main substances employed: "White stuff", a mixture of
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causes the submerged surface to be covered with a conditioning film of organic polymers. In the next 24 hours, this layer allows the
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Medical devices often include fan-cooled heat sinks, to cool their electronic components. While these systems sometimes include
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Similarly, another method shown to be effective against algae buildups bounces brief high-energy acoustic pulses down pipes.
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sp.) to attach themselves. Within two to three weeks, the tertiary colonizers—the macrofoulers—have attached. These include
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Biofouling initial process: (left) Coating of submerged "substratum" with polymers. (moving right) Bacterial attachment and
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Almeida, E; Diamantino, Teresa C.; De Sousa, Orlando (2007), "Marine paints: The particular case of antifouling paints",
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surfaces. These coatings create a smooth surface, which can prevent attachment of larger microorganisms. For example,
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Marine fouling is typically described as following four stages of ecosystem development. Within the first minute the
1318:"Fungal Contaminants in Drinking Water Regulation? A Tale of Ecology, Exposure, Purification and Clinical Relevance" 2381: 1832: 1070: 2235: 1714:
Krishnan, S; Weinman, Craig J.; Ober, Christopher K. (2008), "Advances in polymers for anti-biofouling surfaces",
823: 716: 315:. Biofouling can occur in oil pipelines carrying oils with entrained water, especially those carrying used oils, 229: 513: 219: 727:, after which the bottoms and sides of several ships' keels and false keels were sheathed with copper plates. 723:
explicitly as an anti-fouling device but the first experiments were not made until 1761 with the sheathing of
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Lappin-Scott, Hilary M. (2000), "Claude E. Zobell – his life and contributions to biofilm microbiology",
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Biofouling, especially of ships, has been a problem for as long as humans have been sailing the oceans.
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Microbial Biosystems: New Frontiers, Proceedings of the 8th International Symposium on Microbial Ecology
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A general idea of non-toxic coatings. (Coating represented here as light pea green layer.) They prevent
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Lee, TJ; Nakano, K; Matsumara, M (2001). "Ultrasonic irradiation for blue-green algae bloom control".
830:("plexiglas") demonstrate a high correlation between their resistance to bacterial adhesion and their 2542: 2338: 1908:
Feasibility Demonstration of a Pulsed Acoustic Device for Inhibition of Biofouling in Seawater Piping
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With the rise of iron hulls in the 19th century, copper sheathing could no longer be used due to its
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surface topologies similar to the skin of sharks and dolphins, which only offer poor anchor points.
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experiments linking the effectiveness of copper to its solute rate. In the 1930s microbiologist
776:(TBT) and were effective for up to four years. These biotoxins were subsequently banned by the 387:
easiest to detect is tryptophan, which radiates at 350 nm when irradiated at 280 nm.
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There are two classes of non-toxic anti-fouling coatings. The most common class relies on low
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that would inhibit further leaching of active cuprous oxide from the layer under the crust.
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were tried, and in 1860, the first practical paint to gain widespread use was introduced in
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Kirschner, Chelsea M; Brennan, Anthony B (2012), "Bio-Inspired Antifouling Strategies",
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Sievers, Michael; Fitridge, Isla; Dempster, Tim; Keough, Michael J. (20 December 2012).
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Woods Hole Oceanographic Institute (1952), "The History and Prevention of Foulng",
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Sievers, Michael; Fitridge, Isla; Bui, Samantha; Dempster, Tim (6 September 2017).
1536: 1160: 1010: 932: 884: 788: 160: 37: 1575: 1505:"Biofouling leads to reduced shell growth and flesh weight in the cultured mussel" 657:
described the anti-fouling efforts taken in the construction of the great ship of
1975: 1520: 1430: 1385: 1360: 2203: 2143: 1945: 1693: 964: 879: 857: 731: 636: 616: 558:. This compound, however, also suffers from broad toxicity to marine organisms. 551: 481: 380: 316: 292: 191: 268: 2350: 1875: 1214: 831: 796: 765: 735: 517: 501: 417: 408: 257: 241: 164: 144: 2254: 1294: 1666:"Clean Hulls Without Poisons: Devising and Testing Nontoxic Marine Coatings" 1359:
Fitridge, Isla; Dempster, Tim; Guenther, Jana; de Nys, Rocky (9 July 2012).
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Vladkova, T. (2009), "Surface Modification Approach to Control Biofouling",
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and microorganisms from attaching, which prevents large organisms such as
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R. Oliveira; et al. (2001), "Hydrophobicity in Bacterial Adhesion",
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Andersen, Bjørg Marit (2019). "Operation Department: Infection Control".
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The 1960s brought a breakthrough, with self-polishing paints that slowly
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Anti-fouling is the ability of specifically designed materials (such as
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Woods Hole Oceanographic Institute (1952), "The Effects of Fouling",
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The medical industry utilizes a variety of energy methods to address
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Scripps Institution of Oceanography: Probing the Oceans 1936 to 1976
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Capelletti, Raquel Vannucci; Moraes, Ă‚ngela Maria (7 August 2015).
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New hull coatings for Navy ships cut fuel use, protect environment
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International Journal of Environmental Research and Public Health
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adhere to solid surfaces in marine environments. Mussels utilize
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came to mean something that was highly dependable or risk free.
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performance of the vessel, and increases the fuel consumption.
179:, algae, and biofilm "slime". Together, these organisms form a 1607:"Photonic Frontiers: LEDs - UVC LEDs reduce marine biofouling" 860:, or MAPs. The service life of PEG coatings is also doubtful. 685: 620: 2137:
An Assessment of Ablative Organotin Antifouling (AF) Coatings
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Photonic Frontiers: LEDs - UVC LEDs reduce marine biofouling
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is the process of preventing accumulations from forming. In
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showed that the attachment of organisms is preceded by the
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The deipnosophists, or, Banquet of the learned of Athenæus
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One approach to antifouling entails coating surfaces with
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Materials research into superior antifouling surfaces for
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Study of biofouling began in the early 19th century with
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The Arming and Fitting of English Ships of War 1600-1815
2043:, United States department of the Navy, Bureau of Ships 1237:, United States department of the Navy, Bureau of Ships 2095:
Plutarch (February 2002), "Essays and Miscellanies",
1060:"New Hull Coatings Cut Fuel Use, Protect Environment" 2383:
Biofilm community interactions: chance or necessity?
914: 912: 910: 908: 906: 904: 102:, underwater construction, and desalination plants. 2301:, Halifax, Canada: Society for Microbial Ecology, 1940:, IEEE Conference Publications, pp. 227–231, 992:"Modern approaches to marine antifouling coatings" 581:Pulsed laser irradiation is commonly used against 1968:Prevention and Control of Infections in Hospitals 768:, slowly releasing toxins. These paints employed 2411:"General Aspects of Tin-Free Antifouling Paints" 334:Other mechanisms impacted by biofouling include 2010:, Laser Focus World (July 2016) pp. 28–31 1104:Philosophical Transactions of the Royal Society 211:to occur, with both diatoms and bacteria (e.g. 1252:"Sample records for oil-water emulsified fuel" 36:Current measurement instrument encrusted with 1905:Walch, M.; Mazzola, M.; Grothaus, M. (2000), 1788: 1786: 8: 2274:, San Diego, Calif: Tofua Press, p. 225 2243:Journal of Protective Coatings & Linings 355:the frictional effects leading to increased 1181:Biofouling: It's Not Just Barnacles Anymore 1100:"Designing biomimetic antifouling surfaces" 449:from attaching. Larger organisms require a 272:Dead biofouling, under a wood boat (detail) 223:) attaching, initiating the formation of a 122:between 38% and 72% by 2020, respectively. 1173: 1171: 1169: 985: 983: 946: 944: 942: 2484: 1384: 1343: 1333: 1123: 311:cycles of large industrial equipment and 107:toxic biocide paints, or non-toxic paints 51:) have covered (fouled) the sheath of an 2098:The Complete Works of Plutarch, Volume 3 2054:Culver, Henry E.; Grant, Gordon (1992), 799:of organic compounds now referred to as 542:. The biocides prevent the formation of 379:manufacturers have developed a range of 2029: 2027: 2025: 2023: 2021: 2019: 1203:Chemical & Engineering News Archive 1093: 1091: 900: 47:Plant organisms, bacteria and animals ( 27:Growth of marine organisms on surfaces 1246: 1244: 139:formation and bacterial adhesion—and 7: 2555:10.1146/annurev-matsci-070511-155012 2467:Dalsin, J.; Messersmith, P. (2005). 1053: 1051: 1049: 1047: 1022: 1020: 711:in preparation for cleaning the hull 2534:Annual Review of Materials Research 2167:International Maritime Organization 2159:Focus on IMO - Anti-fouling systems 990:L.D. Chambers; et al. (2006). 778:International Maritime Organization 604:issues associated with biofouling. 109:) to remove or prevent biofouling. 2469:"Bioinspired antifouling polymers" 1482:10.1023/b:aqui.0000013310.17400.97 801:extracellular polymeric substances 25: 2236:"Redefining Antifouling Coatings" 2037:Marine Fouling and its Prevention 1231:Marine Fouling and its Prevention 1178:Stanczak, Marianne (March 2004), 643:(1500–300 BC). Wax, tar and 480:. Low surface energies result in 197:extracellular polymeric substance 147:(hard) fouling organisms include 953:Marine and Industrial Biofouling 772:("tin-based") biotoxins such as 516:to develop environmentally safe 453:to attach, which is composed of 1605:Venugopalan, Hari (July 2016). 1098:Salta, M.; et al. (2008). 999:Surface and Coatings Technology 955:, Springer Series on Biofilms, 875:Biomimetic antifouling coatings 2268:Shor, Elizabeth Noble (1978), 1716:Journal of Materials Chemistry 1670:Journal of Coatings Technology 1664:Brady, R.F. (1 January 2000), 1161:10.1016/j.porgcoat.2007.01.017 1011:10.1016/j.surfcoat.2006.08.129 933:10.1016/j.porgcoat.2003.06.001 684:; "Black stuff", a mixture of 534:Biomimetic antifouling coating 1: 2486:10.1016/S1369-7021(05)71079-8 1576:10.1080/08927014.2017.1361937 1027:Vietti, Peter (4 June 2009), 209:process of bacterial adhesion 2083:Volume I, Book V, Chapter 40 1976:10.1007/978-3-319-99921-0_35 1815:10.1016/0025-326X(94)00181-8 1521:10.1080/08927014.2012.749869 1431:10.1080/08927014.2013.856888 1386:10.1080/08927014.2012.700478 1149:Progress in Organic Coatings 921:Progress in Organic Coatings 703:Ships brought ashore on the 556:dichlorooctylisothiazolinone 307:spiral wound membranes) and 2204:10.1039/9781849730822-00111 2196:Metal Ions in Life Sciences 1946:10.1109/OCEANS.1986.1160543 1275:Journal of Water and Health 965:10.1007/978-3-540-69796-1_7 2597: 1033:, Office of Naval Research 664:A recorded explanation by 565: 550:. Formerly, the so-called 527: 2351:10.1080/08927010500484854 2115:, Conway Maritime Press, 1876:10.1080/09593332208618270 1795:Marine Pollution Bulletin 1462:Aquaculture International 1215:10.1021/cen-v076n017.p041 824:high-density polyethylene 230:Enteromorpha intestinalis 205:van der Waals interaction 2234:Swain, Geoffrey (1999). 2077:Athenaeus of Naucratis, 1058:Vietti, P. (Fall 2009). 514:Office of Naval Research 416:surface with the use of 339:is often removed with a 220:Pseudomonas putrefaciens 2135:Dowd, Theodore (1983). 1069:: 36–38. 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486:fluoropolymers 463:microorganisms 434: 431: 429: 426: 420:, or creating 409:biodispersants 397: 394: 392: 389: 369: 366: 329:hydraulic oils 325:emulsification 313:power stations 265: 262: 188: 185: 127: 124: 120:sulfur dioxide 76:microorganisms 53:electric cable 26: 24: 14: 13: 10: 9: 6: 4: 3: 2: 2593: 2582: 2579: 2577: 2574: 2572: 2569: 2568: 2566: 2556: 2552: 2548: 2544: 2540: 2536: 2535: 2529: 2528: 2524: 2516: 2512: 2508: 2504: 2496: 2493: 2487: 2482: 2478: 2474: 2470: 2463: 2460: 2445: 2441: 2437: 2433: 2429: 2425: 2421: 2420: 2412: 2405: 2402: 2398: 2392: 2385: 2384: 2376: 2373: 2368: 2364: 2360: 2356: 2352: 2348: 2344: 2340: 2336: 2332: 2324: 2321: 2310: 2308:9780968676332 2304: 2297: 2296: 2288: 2285: 2273: 2272: 2264: 2261: 2256: 2252: 2248: 2244: 2237: 2230: 2227: 2223: 2219: 2215: 2213:9781847551771 2209: 2205: 2201: 2197: 2190: 2187: 2172: 2168: 2161: 2160: 2153: 2150: 2145: 2142: 2138: 2131: 2128: 2124: 2118: 2114: 2107: 2104: 2100: 2099: 2091: 2088: 2084: 2080: 2074: 2071: 2067: 2061: 2057: 2050: 2047: 2039: 2038: 2030: 2028: 2026: 2024: 2022: 2020: 2016: 2013: 2009: 2003: 2000: 1995: 1991: 1987: 1981: 1977: 1973: 1969: 1962: 1959: 1955: 1951: 1947: 1943: 1939: 1932: 1929: 1914: 1910: 1909: 1901: 1898: 1893: 1889: 1885: 1881: 1877: 1873: 1869: 1865: 1862:(4): 383–90. 1861: 1857: 1850: 1847: 1834: 1830: 1824: 1821: 1816: 1812: 1808: 1804: 1800: 1796: 1789: 1787: 1783: 1779: 1775: 1771: 1767: 1763: 1759: 1755: 1751: 1747: 1743: 1736: 1733: 1729: 1725: 1721: 1717: 1710: 1707: 1695: 1691: 1687: 1683: 1679: 1675: 1671: 1667: 1660: 1657: 1653: 1649: 1645: 1641: 1637: 1633: 1632: 1624: 1621: 1616: 1612: 1608: 1601: 1598: 1593: 1589: 1585: 1581: 1577: 1573: 1569: 1565: 1561: 1557: 1553: 1546: 1543: 1538: 1534: 1530: 1526: 1522: 1518: 1515:(1): 97–107. 1514: 1510: 1506: 1499: 1496: 1491: 1487: 1483: 1479: 1475: 1471: 1467: 1463: 1456: 1453: 1448: 1444: 1440: 1436: 1432: 1428: 1424: 1420: 1416: 1412: 1404: 1401: 1396: 1392: 1387: 1382: 1378: 1374: 1370: 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retrieved 2444:the original 2423: 2417: 2404: 2382: 2375: 2337:(1): 11–21. 2334: 2330: 2323: 2312:, retrieved 2294: 2287: 2276:, retrieved 2270: 2263: 2249:(9): 26–35. 2246: 2242: 2229: 2195: 2189: 2178:, retrieved 2171:the original 2158: 2152: 2136: 2130: 2112: 2106: 2097: 2090: 2078: 2073: 2055: 2049: 2036: 2007: 2002: 1967: 1961: 1937: 1931: 1920:, retrieved 1913:the original 1907: 1900: 1859: 1855: 1849: 1837:. 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169:tube worms 167:and other 165:polychaete 145:Calcareous 68:Biofouling 2576:Pollution 2255:210981215 2144:ADA134019 2012:StackPath 1954:110171493 1778:205233845 1690:137350868 1295:1477-8920 843:bufotoxin 766:hydrolyze 755:Liverpool 725:HMS Alarm 715:In 1708, 694:shipworms 674:train oil 655:Athenaeus 645:asphaltum 613:plastic. 602:bioburden 447:barnacles 422:nanoscale 368:Detection 251:tunicates 153:bryozoans 149:barnacles 94:epibiosis 2440:12964877 2359:16551557 2222:20877806 1994:86654083 1892:22704787 1884:11329801 1770:20217815 1652:20518560 1631:Langmuir 1584:28876130 1529:23256892 1490:23263016 1447:13421038 1439:24401014 1395:22775076 1303:26837830 1134:20855318 1067:Currents 864:See also 709:careened 666:Plutarch 544:biofilms 524:Biocides 490:biofilms 476:and low 474:friction 455:proteins 443:proteins 428:Coatings 323:through 236:Ulothrix 177:hydroids 159:such as 157:mollusks 2581:Ecology 2571:Fouling 2543:Bibcode 2367:5810987 2339:Bibcode 1864:Bibcode 1839:10 June 1803:Bibcode 1750:Bibcode 1592:3490706 1564:Bibcode 1537:6743798 1470:Bibcode 1419:Bibcode 1373:Bibcode 1345:5486322 1112:Bibcode 870:Fouling 854:mussels 839:Bufalin 822:(PVC), 627:History 583:diatoms 530:Biocide 451:biofilm 391:Methods 255:sessile 225:biofilm 173:seaweed 137:biofilm 126:Biology 88:animals 2453:23 May 2438:  2393:  2365:  2357:  2314:23 May 2305:  2278:21 May 2253:  2220:  2210:  2180:22 May 2119:  2062:  1992:  1982:  1952:  1922:21 May 1890:  1882:  1776:  1768:  1700:22 May 1688:  1650:  1590:  1582:  1535:  1527:  1488:  1445:  1437:  1393:  1342:  1301:  1293:  1187:21 May 1132:  1080:6 June 1037:21 May 971:  789:Davy's 682:sulfur 461:, and 327:, and 264:Impact 163:, and 80:plants 2447:(PDF) 2414:(PDF) 2387:(PDF) 2363:S2CID 2299:(PDF) 2239:(PDF) 2174:(PDF) 2163:(PDF) 2041:(PDF) 1990:S2CID 1950:S2CID 1916:(pdf) 1888:S2CID 1774:S2CID 1686:S2CID 1588:S2CID 1533:S2CID 1486:S2CID 1443:S2CID 1235:(PDF) 1074:(PDF) 1063:(PDF) 995:(PDF) 690:pitch 678:rosin 548:algae 84:algae 61:Lille 57:DeĂ»le 2455:2012 2436:PMID 2391:ISBN 2355:PMID 2316:2012 2303:ISBN 2280:2012 2251:OCLC 2218:PMID 2208:ISBN 2182:2012 2141:DTIC 2117:ISBN 2060:ISBN 1980:ISBN 1924:2012 1880:PMID 1841:2017 1766:PMID 1702:2012 1648:PMID 1580:PMID 1525:PMID 1435:PMID 1391:PMID 1299:PMID 1291:ISSN 1189:2012 1130:PMID 1082:2011 1039:2012 969:ISBN 841:, a 826:and 707:and 688:and 680:and 639:and 532:and 508:and 357:drag 348:HEPA 303:and 297:e.g. 282:drag 115:drag 2551:doi 2511:doi 2507:116 2481:doi 2428:doi 2424:103 2347:doi 2200:doi 2085:ff. 1972:doi 1942:doi 1872:doi 1811:doi 1758:doi 1724:doi 1678:doi 1640:doi 1572:doi 1517:doi 1478:doi 1427:doi 1381:doi 1340:PMC 1330:doi 1283:doi 1211:doi 1157:doi 1120:doi 1108:368 1007:doi 961:doi 929:doi 686:tar 621:DNA 617:UVC 381:UVC 377:LED 70:or 59:in 2567:: 2549:, 2539:42 2537:, 2505:. 2475:. 2471:. 2434:, 2422:, 2416:, 2361:. 2353:. 2345:. 2335:22 2333:. 2247:16 2245:. 2241:. 2216:, 2206:, 2165:, 2139:. 2081:, 2018:^ 1988:. 1978:. 1948:, 1886:. 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Index

Antifouling

zebra mussels

freshwater sponges
electric cable
Deûle
Lille
microorganisms
plants
algae
animals
epibiosis
food processing
toxic biocide paints, or non-toxic paints
drag
sulfur dioxide
biofilm
Calcareous
barnacles
bryozoans
mollusks
zebra mussels
polychaete
tube worms
seaweed
hydroids
fouling community

extracellular polymeric substance

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