• 专利附录
  • 专利说明
  • 权利要求
  • 类似技术
  • 同族专利
  • 引用文献
  • 法律状态
  • 优先权
    • 专利摘要:
    The invention relates to methods and systems for treating an underwater surface (S) and material removed from it at a cleaning site. The underwater surface is cleaned with a brush device (1) by which solid material containing waste water removed from the underwater surface is directed to a treatment unit (5), in which the waste water is separated and filtered. At a first stage, the solid material in the waste water is separated from the waste water, whereupon in a second stage, which immediately follows the first stage, the waste water undergoes a precipitation, and then in the third stage the waste water is filtered. The filtered waste water is conducted at the cleaning site directly back to the watercourse or to another clean water connection. The waste water can be further filtered and / or disinfected if necessary.
    公开号:FI20175684A1
    申请号:FI20175684
    申请日:2017-07-13
    公开日:2019-01-14
    发明作者:Mauri Kalliomäki
    申请人:Dg Diving Group Ltd；
    IPC主号:
    专利说明:

    A method and system for treating an underwater surface and material removed therefrom
    Technical field
    The present invention relates to a method for treating an underwater surface and material removed therefrom at a cleaning site, which method comprises cleaning the underwater surface with a brushing device, and discharging solids containing solids removed from the underwater surface during cleaning to a treatment unit provided with a separator and filtration device. The invention also relates to a system for treating an underwater surface and material removed therefrom and a protective housing, trailer, vehicle and water vehicle comprising the system.
    Prior art
    Treatment of underwater surfaces with various types of brush devices is known. Such an underwater surface may be, for example, the underwater hull, side or bottom of a vessel, from which it is desirable to remove the bottom vegetation, marine fauna and other contaminants formed therein. This type of pollutant causes a great deal of friction as the ship moves in the water, which also significantly increases the ship's fuel consumption. Failure to carefully remove such benthos and marine fauna can also result in unwanted spread of non-native species.
    Such underwater surfaces also often have coatings or paints, such as antifouling and poisonous paints, which, when cleaned, peel off and cause chemical contamination of the water.
    For example, brush devices are disclosed in FR 2 534 548, WO 2011/015786, GB 2 131 288, US 2012/0006244, US 2004/0194237 and US 9,505,472.
    Increasingly stringent environmental regulations impose their own restrictions on the treatment of underwater surfaces.
    Also, the cleaning of underwater surfaces has been proposed to be carried out in an effort to reduce the release of released material into the surrounding water. According to US 7,905,192, waste water containing material removed by means of a brush device is collected and discharged to a separate treatment unit, where the waste water is purified so that it can be collected in a collection container or transferred to a sewer. Other similar types of solutions are disclosed in US 2014/0237740 and WO 2015/031933. Known apparatus and methods are very complex using multiple-step mechanical and chemical treatments for wastewater treatment. In practice, this also means that the size of the known equipment and its dependence on external operating energy is high.
    Summary of the Invention
    The object of the invention is to eliminate the problems of the prior art and to provide a simple and environmentally efficient procedure whereby the waste water collected during the cleaning of the underwater surface can be returned to the water after treatment at the treatment site. This object is achieved by the method of claim 1 and the system of claim 11.
    The basic idea of the invention is to provide a method for separating solids from waste water so that the remaining waste water is readily available in a space that does not contaminate the water at the treatment site when the waste water is returned to the water. It is therefore a waste water treatment process. This is accomplished by leading the effluent containing the solids removed from the underwater surface to a treatment unit for separating the effluent solids from the effluent in a first step, precipitating the effluent immediately after the first step, and subsequently filtering the effluent filtered in the third step. directly back to water or other clean water connection. This avoids having to separately store and transport wastewater, for example, to a wastewater treatment plant.
    20175684 prh 13 -07- 2017
    Surface treatment is understood to mean, for example, both surface cleaning and grinding, depending on the purpose of the surface in question and the related treatment.
    According to a preferred embodiment, in said first step, the solids contained in the wastewater are separated from the wastewater by screening as intact as possible with a screen structure comprising a treatment unit. Thus, the solids rich in undergrowth adhering to the underwater surface and the Me30 algae are kept as intact as possible in said first step, thereby ensuring that solids separated solids and produces minimal amounts of nitrogen and phosphorus in particular, and possibly other undesirable substances. Completed the first step
    20175684 prh 13 -07-2017 separation is a coarse separation, preferably having a screen structure permeability in the range of 70-100 microns.
    In said first step, the solids separated from the wastewater during the screening are preferably introduced into a separate collection vessel, whereby the solids can be collected in a compact form for possible post-treatment or disposal.
    In said first step, the wastewater separated in connection with the screening is preferably passed through a flow section comprising a treatment unit to a filtration device.
    Preferably, the flow section is provided with a coagulant for precipitating the waste water in said second stage before being introduced into the filtration device. Commercially available commercial coagulants may be used as the coagulant. Examples of coagulants include liquid polyaluminium chloride or granulated slaked lime products.
    Preferably, the filtration device is provided with filters for filtering the wastewater in said third step prior to directing the wastewater at the treatment site directly back to the water body or other inlet. The permeability of the filters is in the range of 5 to 40 microns, preferably in the range of 5 to 15 microns.
    The wastewater is preferably subjected to additional filtration before being discharged directly into the water body or other water interface. This ensures that the waste water can be returned directly to the water, for example if the collected waste water is of lower quality than usual. The permeability of the additional filters is thus selected as necessary.
    Filters and auxiliary filters available are suitable commercially available filters available.
    Further, the wastewater is preferably subjected to disinfection after the wastewater has been filtered in said third step or after further filtration of the wastewater. This provides additional assurance that the waste water can be returned directly to the water or other clean water interface, for example, if the waste water has contained organisms, microorganisms such as bacteria, viruses, and protozoa, etc. Disinfection is preferably performed with a UV disinfectant. The UV sensor in the UV disinfector also enables quality control of the wastewater treatment process.
    20175684 prh 13 -07- 2017
    The brush device is preferably provided with a compressor-driven hydraulic drive for ease of use in marine conditions.
    In particular, when the bottom vegetation and the marine organism are removed from the wastewater as solid as possible, the nitrogen and phosphorus content of the wastewater is not raised to high levels 5, thus restoring the nitrogen and phosphorus content of the wastewater to near normal levels. The wastewater thus precipitated and filtered can be returned directly to the water at the treatment site.
    The aforementioned solids include undergrowth, seaweed, etc. removed from the underwater surface, and possibly paint, rust, or other impurities.
    The features of the system of the invention are set forth in claims 11-20. In practice, the system comprises a brush device and a compressor, a first pumping device and a compact processing unit having a basin section, underneath a flow part and a filtration device, possibly another pumping device and additional filtration equipment, if necessary a disinfectant, and a drainage outlet or outlet. This allows for a lightweight and compact system that can be conveniently placed in, for example, a protective case, trailer, vehicle or craft. This allows the system to be easily moved from one location to another.
    The protective housing, trailer, vehicle and watercraft comprising the system are defined in claims 21-24.
    Brief Description of the Drawings
    The invention will now be described, by way of example only, with reference to the accompanying schematic drawings in which
    Figure 1 illustrates an embodiment of the invention,
    Figure 2 illustrates another embodiment of the invention,
    Figure 3 illustrates an alternative embodiment of the invention,
    Figure 4 shows an example of a brush device comprising the system,
    Figure 5 illustrates an embodiment of a processing unit comprising the system, and
    Figure 6 shows another embodiment of a processing unit comprising the system.
    20175684 prh 13 -07- 2017
    Special Explanation
    Figure 1 illustrates an exemplary embodiment of the method and system of the invention. Reference numeral 80 indicates a substrate whose underwater surface S, e.g., flank 81 or bottom 82, is cleaned. The water limit of vessel 80 is indicated by reference WL. To clean the underwater surface, a brush device 1 is used which is moved along the side 81 of the vessel 80 to clean the underwater surface S from adhering material, e.g., bottom vegetation, marine life or other impurities F. The material removed from the surface S is led from the brush device 1 the wastewater containing solids removed from the underwater surface is treated such that the wastewater can be returned directly to the watercourse V or other clean water inlet VL (indicated by dashed lines), through an outlet 70 or through an outlet. The first pumping device 3 (indicated by the arrow lines) is used to direct the waste water from the brush device 1 through the outlet pipe 2 to the treatment unit 5 (the flow direction of the waste water is indicated by arrow lines). The system is preferably provided with a protective housing 100.
    The brush device 1 according to the invention can also be used, for example, to treat, for example, clean or polish the rudder of a ship 80. The above-mentioned prior art problems and the disadvantages of surface contamination are equally problematic with these. The size of the device can always be adapted to the object being treated, the purpose of the treatment, and the quality and shape of the surface.
    The following briefly describes how the actual underwater surface cleaning is performed with an exemplary brush device, using the side and bottom of the ship as an example.
    For example, the starting point is that the bottom 81 and the bottom 82 of the vessel 80 are contaminated with bottom vegetation, marine fauna or other contaminants F, which impedes the vessel's passage. To clean the vessel, the brush device 1 is brought into the water, for example, under the control of a diver, and placed against the underwater surface S of the vessel 80 to be treated.
    Preferably the brush device 1 is a brush device according to Figure 4, comprising a housing 11 surrounding the brush means 13 and provided with a hydraulic drive 12 for rotating the brush means 13 of the brush device. The hydraulic drive 12 is started. The brush means 13 provided with the bristles are rotated so that the underwater surface S is cleaned. Rotation of the brush means 13 on the underwater surface to be treated S around the brush means 13
    20175684 prh 13 -07- 2017 Within the skirt portion 14 provided in the housing 11 generates a vacuum in the housing 11, the device 1 is absorbed onto the underwater surface S to be treated.
    At the same time, the undergrowth or marine biota F in the area of the underwater surface S covered by the housing 11 is brushed off the surface S. The brush device 1 guides the bulk material together with the water in the housing 11 through the outlet 15 provided in the housing 11 to the outlet tube 2. furthermore, the guides disposed at the outlet 15 of the outlet 15 ensure that the removed material is directed directly to the outlet 15 from where it can be further passed through the outlet 2 to the treatment unit 5 as described above.
    The diver can easily guide the device forward along the underwater surface S using the handles 16 in the device 1. The passage of the device is facilitated by the wheels 17 arranged thereon, the movement of which can be smoothed, for example, by a spring 18.
    In this way, all the removed material and the water entering the housing 11 are completely directed to the outlet 15 and thereafter through the outlet pipe 2 to the treatment unit 5. This ensures a clean and easy-to-use brush device 1 for uncontaminated underwater cleaning of the surrounding water.
    The brush device described above is merely exemplary. Other types of brush devices suitable for the same application can also be used in the system and method of the invention.
    The processing unit 5, which will be described in more detail below with reference to Figure 5 and Figure 6, may be located, as shown in the example of Figure 1, on platform 90, from which the operation of the brush device 1 may also be controlled. The system comprises an outlet 25 connected to a first pumping device 3 for pumping waste water containing solids into the treatment unit 5.
    In addition, as shown in Figure 2, the system as a whole may be located, for example, on a watercraft 110 such as a boat or barge, whereby the cleaning operation may also be performed by a ship 30 further from the sea and not just near the quay. The system is preferably provided with a protective housing 100.
    Alternatively, as shown in Figure 3, the system as a whole may be housed, for example, in a protective housing 100, which is preferably a trailer
    20175684 prh 13 -07- 2017 nun 120 or transported by vehicle 130, or directly to vehicle 130, for example a van. This makes it easy to implement a compact and easily movable assembly that allows you to move the system from one cleaning site to another whenever needed, for example by van or car towed trailer.
    This is particularly advantageous as it allows the system to be easily transported to each cleaning site.
    This avoids complicated, large, and locally available, power-dependent solutions for known cleaning sites.
    In Figures 1 and 2, the first pumping device 3 and the brush device 1 with the outlet pipes 2 are shown to be located outside the protective housing 100. Similarly, in Fig. 3, the brush device 1 with its outlet pipes 2 is shown to be located outside the protective housing 100. Of course, because of the system's portability, the protective case or conveyor means is arranged so that all system components can be transported together.
    The system treatment unit 5 shown in Fig. 5 and Fig. 6 comprises a separating device having a basin-shaped part 51, into which the waste water is led from the brush device 1 through the outlet pipe 2 by the first pumping device 3 (wastewater flow direction indicated by arrow lines). The waste water accumulates in the overflow basin portion 51 such that the waste water leaks over the second 20 edge 52 of the pool portion 51 into a screen structure 53, preferably in the form of an arc screen. As the wastewater JV flows along and through the screen structure 53, in the first step of the process of the invention, a solid remains on top of the screen structure 53, from which the solid is collected in a collecting vessel 54. The permeability of the screen structure 53 is preferably 70-100 microns. The separation performed in the first step of the process of the invention is coarse separation.
    The wastewater JV that flows through the screen structure 53 is discharged to the flow section 55 below the screen structure 53. The flow surface is provided with a precipitant 56 to precipitate the wastewater in the second step immediately following the first step of the process of the invention.
    Commercially available commercial coagulants may be used as the coagulant. Examples of coagulants are liquid polyaluminium chloride or granulated slaked lime products.
    20175684 prh 13 -07- 2017
    In said second step of the process of the invention, the waste water is directed through a precipitating agent 56 through a flow portion 55 to a filtration device 57 located below the flow portion 55, which may for example be in the form of a sink and provided with filters 58.
    In said second step of the process, the precipitated wastewater is filtered in the third step directly following the second step of the process of the invention in a filtration device 57 provided with filters 58. The permeability of the filters is in the range 5-40 microns, preferably in the range 5-15 microns. Filters may be used which are commercially available, suitable filters. In practice, the third step of the process immediately follows the second step of the process as the waste water flows along the flow section 55 to a filtration device 57 located below it.
    The wastewater treated as shown in Figure 5 and filtered in the third step of the process is pumped directly to the water by a second pumping device 59. The waste water is pumped directly from the filtration device 57 to the water body V at the treatment site or to the clean water inlet VL via the outlet pipe 70 or the outlet pipe. This depends on the state in which the effluent is obtained, i.e., in practice, the permeability filters 58 used in the filtration device 57 in the third step of the process.
    As shown in Figure 6, the wastewater is preferably subjected to additional filtration after filtration in the third step of the process, thereby ensuring that more contaminated wastewater is returned to a state where it can be returned directly to the water. In this case, the filtered wastewater in the filtering device 57 is pumped by a second pumping device 59 to a further filtration device 60, from which it can similarly be recycled directly to the water system V or other clean water inlet VL through the outlet pipe 70 or outlet. The permeability of the additional filters is thus selected as necessary. Available commercially available filters are used.
    The solids include bottom vegetation, marine life, etc. and possibly, for example, 30 paints, rust, or other impurities.
    To eliminate foreign organisms, wastewater can be filtered with filters having a permeability in the above preferred range of 5 to 15 microns.
    20175684 prh 13 -07- 2017
    To eliminate foreign organisms, the waste water may be further disinfected, if necessary, after filtration in the third stage of the process, or after any further filtration.
    The disinfection is preferably carried out with a UV disinfectant.
    If UV disinfection is used, the UV disinfection device 65 is preferably provided either after the filter device 57 according to Figure 5 or after the additional filter device 60 according to Figure 6. Adding a UV disinfectant to the treatment unit 5 does not substantially increase its size, thereby also achieving all of the above and below advantages of the present invention.
    Preferably, the UV disinfection device 65 includes a UV sensor which firstly ensures that sufficient disinfection power is adjusted. Thus, the UV disinfectant can also be used for quality control of the wastewater treatment process of the system of the invention and of its treatment unit 5. The measurement result provided by the UV sensor can be used to evaluate the status of the treated waste water, with the waste water in an appropriate state15 to return it directly to the water body or other clean water connection.
    The UV disinfection apparatus is preferably in the form of a tube. Examples of design values are: UV permeability 40% / 10mm; UV dose 1500J / m 2 ; and 254 nm.
    Alternatively, disinfection may be performed by heat treatment, pasteurisation, reducing the oxygen content of the waste water, and / or feeding an inert gas to the waste water, ozonation, or hydrogen peroxide.
    In accordance with the above, in the method of the present invention, the underwater surface is first cleaned with a brush device, after which waste water containing solids removed from the underwater surface during cleaning is led to a treatment unit.
    According to the invention, the wastewater collected by the brush device is treated in the treatment unit as described above in three main steps.
    In the first step, the solids contained in the wastewater are separated from the wastewater 30 as intact as possible by screening the solids from the wastewater by means of a screen structure 53, preferably an arc screen. This allows the solids to be separately collected in a collection vessel 54. Since solids, especially benthic and marine organisms, are
    20175684 prh 13 -07- 2017 When clean and separated from the rest of the wastewater, it does not dissolve in the wastewater and does not contain excess nitrogen, phosphorus or other undesirable substances.
    In the second step immediately following the first step, the effluent separated from the solid is precipitated by a precipitator 56 equipped with a precipitant 56.
    55, followed by a third step following the second step of the process, the waste water being filtered in a filtering device 57 provided with filters 58.
    This results in a waste water which, e.g. nitrogen and phosphorus levels are acceptable at environmental standards. The waste water can thus be directly returned to the water system without any harm to the environment. Thus, there is no need to transport wastewater separately, for example, to a treatment plant. If necessary, additional filtration and / or disinfection may be carried out on the waste water.
    The process steps described above allow a system whose components can be assembled into a lightweight and compact structure. In practice, the system comprises only a brush device 1 and an associated compressor, an outlet pipe
    2, a first pumping device 3 and a compact processing unit 5 having a basin portion 51, a flow portion 55 and a filtration device 57 thereafter, a second pumping device 59 and optionally a further filtration apparatus 60 and / or a disinfectant 65, and an outlet pipe 70 or outlet.
    This allows for a lightweight and compact system that can be conveniently located, for example, in a protective case 100, a trailer 120, a vehicle 130 or a watercraft 110. This allows the system to be easily moved from one location to another. The system can thus operate independently at the cleaning site.
    In particular, the compact design of the system and the three successive process steps carried out therewith allow for the purification of wastewater meeting the environmental requirements with a short throughput or throughflow time.
    In the first step, the solids separated from the wastewater are relatively small in quantity, so that any subsequent removal of the solids is easy.
    The drawings and the related description are merely intended to illustrate the basic idea of the invention. Details such as, for example, a brush device, pumps, a screen structure, a precipitant, a filtration device, a filtration apparatus, filters, a disinfectant, drainage pipes, etc. may vary within the scope of the appended claims.
    权利要求:
    Claims (24)
    [1]
    A method for treating an underwater surface and material removed therefrom at a cleaning site, the method comprising cleaning the underwater surface with a brush device and blasting the underwater surface with a brush device.
    5, the effluent containing the solids removed is led to a treatment unit provided with a separating device and a filtration device, characterized in that the effluent containing the solids removed from the underwater surface is discharged to a treatment unit, in which the first 10 in a step, the wastewater is precipitated and then in a third step, the wastewater is filtered, and wherein the filtered wastewater is recycled directly to the water body or other clean water connection at the treatment site.
    [2]
    Method according to claim 1, characterized in that said
    In the first step, the solids contained in the wastewater are separated from the wastewater by screening as intact as possible by means of a sieve structure comprised by the treatment unit.
    [3]
    Method according to claim 1 or 2, characterized in that, in said first step,
    The separated solids are led to a separate collection container.
    [4]
    A method according to any one of the preceding claims, characterized in that, in said first step, the waste water separated during screening is led through a flow section comprising a treatment unit to a filtration device.
    25
    [5]
    A method according to any one of the preceding claims, characterized in that the flow section is provided with a precipitating agent for precipitating the waste water in said second stage before being introduced into a filtration device.
    [6]
    Method according to one of the preceding claims, characterized in that the filtration device is provided with filters for filtering waste water.
    30 in said third stage prior to being discharged directly back into a water body or other water interface.
    [7]
    Method according to one of the preceding claims, characterized in that the effluent is subjected to additional filtration before it is discharged directly back into a water body or other water interface.
    35
    [8]
    Method according to one of the preceding claims, characterized in that the waste water is disinfected after the waste water has been filtered in said third step or after further filtration of the waste water.
    [9]
    Method according to Claim 8, characterized in that the disinfection is carried out with a UV disinfectant.
    20175684 prh 13 -07- 2017
    [10]
    10. A method according to any one of the preceding claims, characterized in that the brush device is provided with a hydraulic drive operated by a compressor.
    [11]
    A system for treating an underwater surface and material removed therefrom at a cleaning site, comprising a brush device (1) for cleaning the underwater surface (S) and a treatment unit (5) for treating wastewater containing solids removed from the underwater surface, comprising a first pumping device (3) for introducing the waste water through the outlet pipe (2) to a waste water treatment unit comprising a separating device and a filtration device (57), characterized in that the separating device is arranged in a first step for separating the solids contained in the wastewater from the wastewater; the filtration device (57) is arranged in a third step to filter the waste water so that the filtered waste water can be led directly to the treatment site n waterways or other clean water connections.
    [12]
    System according to claim 11, characterized in that the separating device comprises a basin-like part (51) to which the waste water is fed, wherein the basin-like part has a screen structure (53) for separating the solid from the wastewater in said first step.
    [13]
    System according to Claim 11 or 12, characterized in that a collecting vessel (54) is arranged in connection with the separating device for receiving the separated solids in the separating device.
    [14]
    A system according to any one of claims 11 to 13, characterized in that the precipitation device comprises a separating device (55) in connection with the basin section (51) for introducing waste water into the filtration device (57) in said second step.
    [15]
    A system according to any one of claims 11 to 14, characterized in that the flow section (55) is provided with a precipitating agent (56) for precipitating the waste water in said second stage before introducing the waste water into the filtration device (57).
    [16]
    System according to one of Claims 11 to 15, characterized in that the filtration device (57) is provided with filter elements (58) for filtering the waste water in said third step.
    [17]
    A system according to any one of claims 11 to 16, characterized in that the system comprises an additional filtration apparatus (60).
    [18]
    A system according to any one of claims 11 to 17, characterized in that the system comprises a disinfectant (65).
    [19]
    A system according to claim 18, characterized in that the disinfecting device (65) is a UV disinfecting device.
    [20]
    System according to one of Claims 11 to 19, characterized in that the brush device (1) is equipped with a hydraulic drive (12) operated by a compressor.
    [21]
    A protective housing comprising a system according to any one of claims 11 to 20.
    [22]
    A trailer comprising a system according to any one of claims 11 to 20.
    [23]
    A vehicle comprising a system according to any one of claims 11 to 20.
    [24]
    A water vehicle comprising a system according to any one of claims 11 to 20.
    类似技术:
    公开号 | 公开日 | 专利标题
    US5466367A|1995-11-14|Industrial waste water treatment
    JP2007534543A5|2008-06-19|
    WO1993007956A1|1993-04-29|Process for removing arsenic from water
    MXPA06012268A|2007-03-15|Wastewater treatment.
    EP1546042A2|2005-06-29|Process and device for the treatment of water, particularly for ships
    US20150108071A1|2015-04-23|De-ballast filtration
    US10240312B2|2019-03-26|Aquatic contaminator elimination device
    WO2007142068A1|2007-12-13|Purification apparatus for ship ballast water
    KR20160105629A|2016-09-07|System for hull cleaning of ship
    RU2681458C2|2019-03-06|Plant for the treatment of waste water on board of vessels
    FI128075B|2019-09-13|Method and apparatus for treating an underwater surface and the matter removed from it
    JP6291527B2|2018-03-14|Circulating water treatment equipment
    KR20140103609A|2014-08-27|Apparatus for treating sewage in ship and fish farm
    Nguyen et al.2019|A case study of low pressure air flotation ferryboat for algae removal in Korean rivers and lakes
    JP4374830B2|2009-12-02|Purified water supply system
    US20140346125A1|2014-11-27|Desalting Salty Sludge System and Method
    JP2005349259A|2005-12-22|Liquid detoxification method and its apparatus
    CN101973369A|2011-02-16|Multifunctional water environment disaster emergency treatment ship and water pollution treatment method using same
    KR100696604B1|2007-03-19|System and Method for Treating Discharge Water of Industrial Facility
    US20210371314A1|2021-12-02|Systems and methods for hull wastewater remediation
    KR100529536B1|2005-11-17|A sedimentation matters removal apparatus of the sea-bottom and the reservoir capable of continuous process
    JP2004073946A|2004-03-11|Method of purifying sludge at bottom of water
    IL245507A|2021-02-28|Method comprising separation and high voltage pulse treatment before digestion or further purification
    KR19990079000A|1999-11-05|Sewage Treatment Facility with Nano Filtration Membrane
    EP2855361B1|2016-07-20|De-ballast filtration
    同族专利:
    公开号 | 公开日
    FI20175684A|2019-01-14|
    EP3652059A1|2020-05-20|
    WO2019012184A1|2019-01-17|
    FI128075B|2019-09-13|
    US20210114896A1|2021-04-22|
    引用文献:
    公开号 | 申请日 | 公开日 | 申请人 | 专利标题
    GB2131288B|1982-10-06|1986-02-05|Mitsui Shipbuilding Eng|Apparatus for cleaning underwater surfaces|
    FR2534548B1|1982-10-18|1985-02-01|Ritm|
    NL1019765C2|2002-01-17|2003-07-18|Hendrikus Andreas Pet Schollen|Device for inspecting and environmentally friendly mechanical / hydraulic cleaning of underwater surfaces of vessels, swimming pools, aquariums and the like.|
    US20040194237A1|2003-04-04|2004-10-07|Walton Charles A.|Underwater cleaning apparatus using suction grip|
    US7534357B2|2005-03-28|2009-05-19|Navalis Environmental Systems, Llc|Dual-train wastewater reclamation and treatment system|
    US7905192B1|2006-11-03|2011-03-15|The United States Of America As Represented By The Secretary Of The Navy|Integrated underwater surface cleaning and effluent treatment system|
    FR2948920B1|2009-08-05|2013-08-16|Jean Claude Kempen|CLEANING ROBOT OF CARENES OF BOATING BOATS WITH FLOT|
    US20120006244A1|2010-07-12|2012-01-12|Van Rompay Boudewijn Gabriel|Recuperation system for underwater cleaning operations|
    US9073614B2|2013-02-28|2015-07-07|Carl Nettleton|Device and system for cleaning a surface in a marine environment|
    FI125878B|2013-06-13|2016-03-31|Dg Diving Group Ltd|Apparatus and method for treating underwater surfaces|
    KR102207601B1|2013-09-04|2021-01-27|쥐알디 프랜마린 홀딩스 피티와이 엘티디|A marine cleaning system|ES2881849A1|2020-05-27|2021-11-30|Gonzalez Batanero Diego|Equipment for the disinfection and inerting of biological species for its application in cleaning floating and fixed structures in aquatic environments, ships, polishing propellers, ballast tanks, and water filtering systems. |
    法律状态:
    2019-09-13| FG| Patent granted|Ref document number: 128075 Country of ref document: FI Kind code of ref document: B |
    优先权:
    申请号 | 申请日 | 专利标题
    FI20175684A|FI128075B|2017-07-13|2017-07-13|Method and apparatus for treating an underwater surface and the matter removed from it|FI20175684A| FI128075B|2017-07-13|2017-07-13|Method and apparatus for treating an underwater surface and the matter removed from it|
    EP18755853.1A| EP3652059A1|2017-07-13|2018-07-11|Method and system for treatment of an underwater surface and material removed from it|
    US16/634,518| US20210114896A1|2017-07-13|2018-07-11|Method And System For Treatment Of An Underwater Surface And Material Removed From It|
    PCT/FI2018/050541| WO2019012184A1|2017-07-13|2018-07-11|Method and system for treatment of an underwater surface and material removed from it|
    [返回顶部]