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GB2459854A - Anti-fouling apparatus using a gas permeable membrane and a gas - Google Patents

Anti-fouling apparatus using a gas permeable membrane and a gas Download PDF

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Publication number
GB2459854A
GB2459854A GB0808211A GB0808211A GB2459854A GB 2459854 A GB2459854 A GB 2459854A GB 0808211 A GB0808211 A GB 0808211A GB 0808211 A GB0808211 A GB 0808211A GB 2459854 A GB2459854 A GB 2459854A
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United Kingdom
Prior art keywords
gas
micro
environment
fouling
gas permeable
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
GB0808211A
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GB0808211D0 (en
Inventor
Jeremy Thomason
Thomas Vance
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Newcastle University of Upon Tyne
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Newcastle University of Upon Tyne
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Newcastle University of Upon Tyne filed Critical Newcastle University of Upon Tyne
Priority to GB0808211A priority Critical patent/GB2459854A/en
Publication of GB0808211D0 publication Critical patent/GB0808211D0/en
Priority to PCT/GB2009/050474 priority patent/WO2009136197A2/en
Publication of GB2459854A publication Critical patent/GB2459854A/en
Withdrawn legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B63SHIPS OR OTHER WATERBORNE VESSELS; RELATED EQUIPMENT
    • B63BSHIPS OR OTHER WATERBORNE VESSELS; EQUIPMENT FOR SHIPPING 
    • B63B59/00Hull protection specially adapted for vessels; Cleaning devices specially adapted for vessels
    • B63B59/04Preventing hull fouling
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B08CLEANING
    • B08BCLEANING IN GENERAL; PREVENTION OF FOULING IN GENERAL
    • B08B17/00Methods preventing fouling
    • B08B17/02Preventing deposition of fouling or of dust
    • CCHEMISTRY; METALLURGY
    • C23COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; CHEMICAL SURFACE TREATMENT; DIFFUSION TREATMENT OF METALLIC MATERIAL; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL
    • C23FNON-MECHANICAL REMOVAL OF METALLIC MATERIAL FROM SURFACE; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL; MULTI-STEP PROCESSES FOR SURFACE TREATMENT OF METALLIC MATERIAL INVOLVING AT LEAST ONE PROCESS PROVIDED FOR IN CLASS C23 AND AT LEAST ONE PROCESS COVERED BY SUBCLASS C21D OR C22F OR CLASS C25
    • C23F15/00Other methods of preventing corrosion or incrustation
    • C23F15/005Inhibiting incrustation
    • EFIXED CONSTRUCTIONS
    • E02HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
    • E02BHYDRAULIC ENGINEERING
    • E02B17/00Artificial islands mounted on piles or like supports, e.g. platforms on raisable legs or offshore constructions; Construction methods therefor
    • E02B17/0017Means for protecting offshore constructions

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  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Civil Engineering (AREA)
  • Structural Engineering (AREA)
  • Combustion & Propulsion (AREA)
  • Ocean & Marine Engineering (AREA)
  • Materials Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Paints Or Removers (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)
  • Physical Or Chemical Processes And Apparatus (AREA)
  • Catching Or Destruction (AREA)
  • Prevention Of Fouling (AREA)

Abstract

An anti-fouling apparatus 1 comprises a gas permeable element 3 attachable to a surface and means 4 and 5 to introduce gas 6 to the gas permeable element. The gas is released into a micro-environment immediately adjacent the free surface of the gas permeable element and the gas is selected to modify at least one condition in the micro-environment, such that the micro-environment is rendered unfavourable to the accumulation of foulants therein. The gas may contain carbon dioxide, nitrogen, chlorine, ozone or a noble gas. The gas may react with sea water 2 to reduce the pH of the sea water in the micro-environment. The gas permeable element may include one of a gas permeable membrane, a micro-porous layer, a gas permeable solid, a gas chamber, a perforated pipe or an air stone. A structure protected by the anti-fouling apparatus and a method for its use, are also disclosed.

Description

Environmental Control of Fouling
Field of the Invention
The invention relates to an apparatus and method for controffing fouling and in particular to an apparatus and method which controls marine fouling by modifying the environment around a surface.
Background of the Invention
Marine fouling is the undesirable accumulation of biological and/or inorganic matter on the surfaces of structures submerged in the sea. It can be divided into two main groups: namely microfouling and macrofouling, which together form a fouling community. Examples of microfouling include bacterial adhesion and the formation of biofilms or slime, as well as the crystaffisation of salts, oxides and hydroxides known as scaling. Macrofouling, on the other hand, is the attachment of larger organisms such as barnacles, mussels, worms, sea squirts, bryozoans and seaweed but also includes plant matter and manmade refuse. Biofouling or biological fouling is most problematic and affects both static and mobile structures. The growth of slime and larger organisms is a particular problem for ships where such growth can form an enormous mass on the hull and diminish the ship's speed, manoeuvrabiJity and carrying capacity, as well as increasing fuel consumption and corrosion. This is more severe on naval vessels since they are usually moored for long periods of time, where the formation of slime alone can reduce fuel consumption by up to 2%.
As a result, governments and industry currently spend billions of pounds a year trying to control biofouling.
In order to minimise the impact of biofouling, many underwater structures are protected by antifouling coatings containing biocides which are toxic to marine fouling organisms. In the early days of sailing ships, lime, copper sheets, and later arsenic were used to coat the ship's hull until the modern chemical industry developed antifouling paints using biocidal compounds. Compounds commonly used in antifouling paints include cuprous oxide, metallic copper, and until recently tn-butyl-tin oxide (TBT) and other organic biocides such as zinc pyrithione. These compounds, however, are designed to dissolve in a controlled manner to release the biocide over a period of time.
This reduces the effectiveness of the coating, and as a result, they have to be reapplied in regular intervals, in some cases as often as every 5 months. More importantly, studies have shown that the compounds can persist in the water for long periods of time, kiffing non-target sealife, harming the environment and possibly entering the food chain. Furthermore, these coatings are rarely completely effective against all forms of fouling, and even on modern biocidal coatings, slime films form. The US navy have since called for an antifouling agent which is both non-toxic and has a 12 year life span.
The International Convention on the Control of Harmful Antifouling Systems on Ships set up by the International Maritime Organisation (IMO) was adopted in October 2001 and comes into force in September 2008. This convention prohibits the use of harmful substances in antifouling paints used on ships. Under the terms of the convention, member states are required to prohibit and/or restrict the use of harmful antifouling systems on ships flying their flag, as well as ships which operate under their authority and those that enter their ports, shipyards and offshore terminals. The ban of these compounds presents a severe problem for the shipping industry. A major challenge, therefore, is to develop alternative technologies to prevent and treat biofouling, and to date, a number of different solutions have been proposed: The use of electrochemical apparatus is described in EP0985639 and JP2000008338. This method involves the passage of a dc current through a conductive coating on the surface of the submerged structure to kill off any bacteria and overlying organisms. However, fine control of the applied potential is necessary to avoid the production of harmful chlorine gas when sea water is
I
A-
electrolysed. With ships, care is also needed to prevent the current from passing through the underlying hull and dissolving it.
A different solution described in US4046094 uses a continuous flow of fresh water and an opaque curtain to discourage and inhibit the growth of biological material on a ship's hull. The curtain shields the fresh water from the mixing action of ocean currents and also acts to block out sunlight. This method would appear to be very impractical for a large ocean going vessel.
US655 1536 describes a reverse osmosis membrane containing titanium dioxide particles. In this invention, titanium dioxide is used as a photo catalyst that decomposes organic contaminants and kills microorganisms when exposed to UV or solar radiation. When biofoulants attach to the membrane they are destroyed, without the production of any harmful bi-products. This technique has applications in water purification systems but is unsuitable for coating the hull of a ship.
Several non-toxic silicone-based coatings have been developed which make the surfaces of mobile structures sufficiently slippery that fouling organisms have difficulty attaching themselves and are washed off as the structure moves through the water. Although these coatings are implied to have no limited lifespan, they gradually foul, and have to be cleaned periodically. They are also unsuitable for use on static structures.
Summary of the Invention
When carbon dioxide mixes with sea water, carbonic acid is initially formed (equation 1).
The two hydrogen atoms of carbonic acid then dissociate from the parent molecule in turn to form bicarbonate or hydrogen carbonate (equation 2) and carbonate (equation 3). It has been found that the low pH of carbonic acid creates an inhospitable environment for marine organisms inhibiting their growth. However, as carbonic acid is non-toxic in low concentrations, occurs naturally in seawater and is quickly buffered, there is no adverse environmental legacy.
(1) Co2 + H20 H2C03 (2) H2C03 � HCO + H (3) HCO!= CO + W The invention provides a simple apparatus and method for controffing marine fouling without contamination of the environment. When used in conjunction with carbon dioxide, a micro-environment in which the pH is lowered is created at the surface around which the carbon dioxide is released. This is able to keep the surfaces of structures submerged in static, fully marine water clear of visible marine fouling.
Based on the results of field trials, the invention is particularly suited to preventing the formation of slime, algae and macro invertebrates on the surfaces of small and large mobile and static structures in marine environments.
The invention is not be limited to carbon dioxide gas, however, but extends to other gases capable of modifying other conditions in the micro-environment and which may be selected such that said micro-environment is rendered unfavourable to the accumulation of a specific foulant. One such example is the release of a noble gas or nitrogen gas to create oxygen-depleted conditions, inhibiting the growth of macro fauna and flora, or aerobic microbes. Also, the invention may use a combination of gases with different properties simultaneously to modify more than one condition in the micro-environment.
Further, whilst the release of carbon dioxide into the marine environment in the amounts required to control fouling is easily buffered, thereby preventing environmental damage, the invention is not limited to the use of gases which do not have an environmental impact The invention may be deployed in a situation where an environmental impact is acceptable and the fouling requires a gas which may result in an environmental impact The gases used in the invention may be supplied from gas canisters or could come from recovered exhaust gases. Large vessels, such as tankers, store scrubbed exhaust gases from engines for use as fire suppressants. Such gases are rich in carbon dioxide and would be suitable for use without any prior purification.
According to the invention, there is provided an anti-fouling apparatus comprising a gas permeable element attachable to a surface and means to introduce gas to the gas permeable element, wherein the gas is released into a micro-environment immediately adjacent the free surface of the gas permeable element and wherein the gas is selected to modify at least one condition in said micro-environment such that the said micro-environment is unfavourable to the accumulation of foulants therein.
According to another aspect of the invention, there is provided a method of modifying at least one condition in a micro-environment such that the micro-environment is rendered unfavourable to the accumulation of foulants therein, the method comprising the steps of: i) releasing a gas into said micro-environment; ii) reacting the gas with at least one constituent of the micro-environment to modify said at least one condition.
This technology is particularly suited to the prevention of fouling on static structures such as oil rigs, cooling water pipe intakes for coastal power stations and desalination plants, windows/sensor housings on remote inteffigent ocean monitoring buoys and land based marine aquaculture systems, whilst likely mobile beneficiaries include ships, submarines and barges. The invention may also be used to prevent calcium carbonate accumulation at the point of entry in domestic and industrial water supplies.
A tie-coat may be used to bond the gas permeable element to the surface of the submerged structure. In general, tie-coats are paints formulated to provide a transition from an undercoat to a topcoat under specific conditions. In this case, the tie-coat could be applied directly to the surface of interest with the gas permeable element fixed on top. The gas permeable element itself might be a gas permeable membrane, a micro-porous layer, a gas permeable solid, a gas chamber, a perforated pipe or an air stone. An air stone is a block of porous material that when fed a source of pressurised gas, diffuses the gas into the water in the form of bubbles.
Whilst most antifouling paints are capable of controffing specific types of fouling material, few are able to prevent all forms of fouling. Also, most of these paints have a limited lifespan as a result of their solubiJity in water and must be reapplied on a regular basis. Even siJicone-based non-toxic coatings which are implied to have no limited lifespan gradually foul and need periodic cleaning. On the other hand, this invention is suitable for controlling all types of marine fouling and has no foreseeable restriction on lifespan.
Brief Description of the Drawings
In the drawings, which illustrate preferred embodiments of the invention and are by way of
example:
Figure 1 is a cross-sectional schematic of the coating according to a first aspect of the invention; Figure 2 is a cross-sectional schematic of the coating according to a second aspect of the invention; Figure 3a is a cross-sectional schematic of a roughened PVC test panel; Figure 3b is a cross-sectional schematic of a PVC test panel coated with a smooth silicone membrane; Figure 3c is a cross-sectional schematic of a PVC test panel with a smooth silicone membrane stretched over PVC support ribs and enclosing a gas space containing carbon dioxide; Figure 4a is a plan view photograph of the test panel in Figure 3a taken immediately after the
month static water field trial;
Figure 4b is a plan view photograph of the test panel in Figure 3b taken immediately after
the 5 month static water field trial;
Figure 4c is a plan view photograph of the test panel in Figure 3c taken immediately after the
month static water field trial;
Figure 5 is a bar chart of the experimental results showing the summed percentage cover of slime formed on each panel type as determined immediately after the 5 month static water field trial; Figure 6 is a bar chart of the experimental results showing the total number of macro fouling species formed on each panel type as determined immediately after the 5 month static water field trial; and Figure 7 is a schematic cross-section of the coating indicating pH as measured at the surface of the membrane and the surrounding water.
Detailed Description of the Preferred Embodiments
Referring now to Figure 1, in one embodiment of the invention there is shown a surface coating 1 submerged in seawater 2, said surface coating 1 comprising of a smooth gas permeable membrane 3 stretched over support ribs 4 and enclosing a gas space 5 containing carbon dioxide 6.
Over time, carbon dioxide gas 6 diffuses through the membrane 3 and reacts with the seawater 2 to produce carbonic acid 7. This in turn lowers the pH at the surface of the membrane which creates inhospitable environmental conditions for the organisms and inhibits their growth.
Referring now to Figure 2, in another embodiment of the invention there is shown a second surface coating 8 applied to a ship's hull 9, said surface coating 8 comprising of a smooth gas permeable membrane 3 adhered to a micro-porous tie-coat 10. The tie-coat 10 is in direct contact with the hull 9 and carbon dioxide gas 6 diffuses from the tie-coat 10 through the membrane 3 and reacts with the seawater 2 to produce carbonic acid 7.
Referring now to Figures 3a, 3b and 3c, there are illustrated cross-sections of PVC test panels with different surfaces designed to study the effects of surface structure and coating on marine fouling. All panels are made from grey PVC of size 10 x 10 x 0.3cm3. The first type of panel 11 has been evenly roughened with coarse sandpaper, the second type 12 has been coated with a 0.15cm thick gas permeable silicone membrane 3 fixed to the PVC with a silicone-based adhesive, whilst the third type 13 has a 0.15cm thick gas permeable silicone membrane 3 stretched over PVC support ribs 4 and industrial grade carbon dioxide gas 6 introduced in the space behind the membrane 3 at a rate of 0.015 1/cm2 /h and a pressure of 0.lbar.
Referring now to Figures 4a, 4b and 4c, there are shown plan view photographs of the test panels in Figures 3a, 3b and 3c respectively, taken immediately after the 5 month static water field trial. Slime 14 and multiple species of macrofouling material (tunicates, worms and bryozoans) 15 are clearly visible on the roughened PVC 11 and silicone coated 12 panels, whilst the panel 13 treated with carbon dioxide appears clean, except for the area above the support ribs where slime and tunicates formed in small quantities.
Figures 5 and 6 show the experimental results of the static water field trial determined at the end of the five month test period. The summed percentage cover of slime formed on each panel type is given in Figure 5, whilst Figure 6 reveals the total number of tunicates, worms and bryozoans as indicated.
Referring now to Figure 7, there is shown a schematic cross-section of the coating 8, indicating pH as measured at the surface of the membrane 3 and the surrounding water 2. At the surface, carbonic acid production reduces the water pH from -8 (substantially neutral) to -5 (acidic) creating a micro-environment that is unfavourable to the accumulation of marine foulants.
Experiment A five month static water field trial was conducted to study the effects of surface structure and coating on marine fouling. Three test panels of each type were randomly arranged on a framework made from PVC tubing, and suspended in a temperate marina at a depth of one meter for five months. The panels were periodically photographed and any marine growth coarsely identified and quantified in terms of percentage cover and the total number of individual organisms.
Results After five months, multi-species marine communities were found to be growing on the roughened PVC and siJicone coated panels, with least growth present on the panels exposed to carbon dioxide. The small amount of fouling present on the latter type of panel was concentrated around the PVC support ribs. Panels covered in the silicone membrane without being exposed to carbon dioxide had a limited antifouling capacity, whilst the test panels made from roughened PVC
Discussion and conclusions
The results of this experiment indicate that carbon dioxide gas permeating through a silicone membrane is capable of preventing the formation of slime, algae and invertebrates on the surfaces of structures submerged in static marine waters for at least five months. That small growth was present on the membrane above the PVC support ribs may be attributed to the fact that the PVC used is not permeable to carbon dioxide, and so this area of the membrane is unlikely to be exposed to the same acidic conditions as the surrounding regions. The difference between the levels of growth on the rough PVC and the smooth silicone coating also suggests that microorganisms favour an irregular surface over a smoother surface. This may be related to an improved adhesion allowing fouling materials to bind to the panel, or could be down to an increase in surface area providing a greater number of inhabitable sites.
Based on the results of these field trials, the invention provides a simple solution for keeping the surfaces of structures submerged in the sea clear of all forms of marine fouling. Such technology is likely to benefit large static and mobile structures including ships, barges, submarines, oil rigs and pipes amongst others.

Claims (16)

  1. Claims 1. An anti-fouling apparatus comprising a gas permeable element attachable to a structure requiring protection from fouling and means to introduce gas to the gas permeable element, wherein the gas is released into a micro-environment immediately adjacent the free surface of the gas permeable element and wherein the gas is selected to modify at least one condition in said micro-environment such that the said micro-environment is rendered unfavourable to the accumulation of foulants therein.
  2. 2. An anti-fouling apparatus according to Claim 1, wherein the gas contains carbon dioxide, nitrogen, chlorine, ozone or a noble gas.
  3. 3. An anti-fouling apparatus according to any preceding claim, wherein the gas is capable of reacting with sea water to reduce the pH thereof in the said micro-environment.
  4. 4. An anti-fouling apparatus according to any preceding claim, wherein the gas permeable element includes at least one of: a gas permeable membrane, a micro-porous layer, a gas permeable solid, a gas chamber, a perforated pipe, and an air stone.
  5. 5. Anti-fouling apparatus according to Claim 3, wherein the gas permeable element includes a gas permeable membrane supported by spaced apart ribs.
  6. 6. Anti-fouling apparatus according to Claim 3, wherein the gas permeable element includes a gas permeable element adhered to the said structure by a tie-coat.
  7. 7. Anti-fouling apparatus according to any preceding claim, further comprising a gas supply.
  8. 8. Anti-fouling apparatus according to any preceding claim, further comprising a gas pressurising means arranged to pressurise gas upstream of the gas permeable element.
  9. 9. A structure requiring protection from fouling and attached thereto apparatus according to any of Claims 1 to 8.
  10. 10. A structure according to Claim 9, wherein the structure may be at least one of the following: oil rig, pipe, buoy, aquaculture system, ship, submarine, sensor or a barge.
  11. 11. A structure according to Claim 9, wherein the structure may be a vessel producing exhaust gases containing carbon dioxide, said vessel incorporating a means for recovering the exhaust gases, wherein the exhaust gases may serve as a source of carbon dioxide for use in apparatus according to any of Claims 1 to 8.
  12. 12. A method of modifying at least one condition in a micro-environment such that the micro-environment is rendered unfavourable to the accumulation of foulants therein, the method comprising the steps of: i) releasing a gas into said micro-environment; ii) reacting the gas with at least one constituent of the micro-environment to modify said at least one condition.
  13. 13. A method according to Claim 12, wherein the condition modified is pH.
  14. 14. A method according to Claim 12, wherein the condition modified is the oxygen content of the said micro-environment.
  15. 15. A method according to Claim 12, wherein the gas contains carbon dioxide, nitrogen, chlorine, ozone or a noble gas.
  16. 16. A method according to Claims 12 to 15, wherein the gas is released into the said micro-environment by means of an apparatus as claimed in any of Claims 1 to 8.
GB0808211A 2008-05-07 2008-05-07 Anti-fouling apparatus using a gas permeable membrane and a gas Withdrawn GB2459854A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
GB0808211A GB2459854A (en) 2008-05-07 2008-05-07 Anti-fouling apparatus using a gas permeable membrane and a gas
PCT/GB2009/050474 WO2009136197A2 (en) 2008-05-07 2009-05-07 Environmental control of fouling

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
GB0808211A GB2459854A (en) 2008-05-07 2008-05-07 Anti-fouling apparatus using a gas permeable membrane and a gas

Publications (2)

Publication Number Publication Date
GB0808211D0 GB0808211D0 (en) 2008-06-11
GB2459854A true GB2459854A (en) 2009-11-11

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GB0808211A Withdrawn GB2459854A (en) 2008-05-07 2008-05-07 Anti-fouling apparatus using a gas permeable membrane and a gas

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WO (1) WO2009136197A2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110220069B (en) * 2019-06-04 2020-07-03 珠海格力电器股份有限公司 Water channel with self-cleaning surface, self-cleaning method thereof and electric appliance

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SU1030255A1 (en) * 1981-09-18 1983-07-23 Zajniddinov Khamidulla T Apparatus for protecting ship hull underwater surface from fouling
US20050087117A1 (en) * 2003-10-28 2005-04-28 Scott Bentley N. Yacht barnacle inhibitor system
WO2008102343A1 (en) * 2007-02-19 2008-08-28 Joshua Waldhorn Apparatus and method for reducing friction, corrosion and biological growth on the hull of marine vessels

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3661506A (en) * 1969-09-03 1972-05-09 Outboard Marine Corp Means and method of eliminating and controlling marine fouling
US4092943A (en) * 1976-07-19 1978-06-06 Norman Lund Marine protection system
PT1699885E (en) * 2003-12-12 2008-10-20 Ecosea Ltd A marine anti-bio-fouling coating and a method of applying the coating
US20070036902A1 (en) * 2005-08-12 2007-02-15 O'neal Hubert R Method for applying chemical coatings

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SU1030255A1 (en) * 1981-09-18 1983-07-23 Zajniddinov Khamidulla T Apparatus for protecting ship hull underwater surface from fouling
US20050087117A1 (en) * 2003-10-28 2005-04-28 Scott Bentley N. Yacht barnacle inhibitor system
WO2008102343A1 (en) * 2007-02-19 2008-08-28 Joshua Waldhorn Apparatus and method for reducing friction, corrosion and biological growth on the hull of marine vessels

Also Published As

Publication number Publication date
WO2009136197A2 (en) 2009-11-12
GB0808211D0 (en) 2008-06-11
WO2009136197A3 (en) 2010-08-19

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