The invention relates to preventing microplastics from entering the environment. In particular the invention is directed to regenerating the pressure consumption of filters for removing microplastics in effluent from any source but in particular removing microfibers from washing machine wastewater.
Microfibres are the most abundant form of microplastic pollution in rivers and oceans. Due to their microscopic scale, microfibers are eaten by organisms at all levels of the food chain, from plankton to top predators. Once ingested, plastics reduce feeding efficiency (false satiation) they may damage the gut of the animal and transfer harmful additives like PCBs, pesticides, flame retardants to the animal that consumed it. Plastics consumed by animals low in the food chain also impact their predators, which consume numerous contaminated prey daily. The pervasiveness of microfibers in the food chain has naturally resulted in concern regarding their transfer to humans, and contamination has been observed in crustaceans, molluscs and fish species destined for human consumption.
Unlike microbeads, which are easily excluded from toiletries and cleaning products, microfibres are formed through damage to clothing. One third of all microplastics in the oceans come from washing of synthetic textiles. Synthetic fabrics derived from petrochemicals make up 65% of all textiles. Wear and tear caused by abrasive forces in washing machines result in the fragmentation of man-made textiles, forming hundreds of thousands of microfibres, less than 5 mm in length, which leak from homes and drainage networks into the ocean.
The vast impact of microplastics on marine ecosystems is starting to be understood. A 2019 study published in the ‘Science of the Total Environment’ journal found 49% of 150 fish samples from the North East Atlantic Ocean contained microplastics with evidence of this causing harm to brain, gills, and dorsal muscles. These microplastics are also passed onto people consuming fish at a rate of between 518-3078 microplastic items/year/capita.
The impact is not just being seen in fish stocks but also algae, the building blocks of life. A 2015 study published in the ‘Aquatic Toxicology’ journal demonstrated high concentrations of polystyrene particles reduced algal growth up to 45%. This should be of concern as microalgae are one of the world's largest producers of oxygen on this planet.
Wastewater treatment plants cannot remove the millions of fibres that pass through them every day. Currently, secondary level water treatment removes around 98% of the microplastics that pass through them. However, the small proportion that escapes still equates to tens of millions of fibres per treatment works per day.
Furthermore, wastewater treatment plants produce a “sewage sludge” and plastic microfibers are found on discharge when released into the natural environment when the sludge is spread on agricultural land, thus microfibers make their way into the food chain, waste to energy (which can destroy fibres but release harmful gasses) or discharged into rivers or the ocean.
Current washing machine filters are designed to stop pennies and buttons breaking the washing machine pump. The filtration required to stop microfibres is less than 50 micrometers (μm), which is about the width of a human hair.
It is known to provide mesh filters that stop the problem at source. However, mesh filters clog up quickly and when this happens their effectiveness drops off considerably. This causes the pressure to drop and the flow rate to reduce, which can lead to damage to pumps and other elements of the system and flooding.
A typical front-loading domestic washing machine is shown in
A typical top-loading machine will have the axis of the drum vertical but will otherwise share many of the features of the front-loading machine.
In use, dirty laundry is placed in the drum, and a wash cycle initiated by a user. The CPU allows cold water to flow via the drawer to mix with detergent and then on into the drum, where the water is heated. The combined water, detergent and laundry is agitated by rotating the drum. During this process, dirt and grease is released into the water and fibres from the clothing too. If the clothing is synthetic, microfibers are typically released as the clothes rub against each other. The resulting effluent at the end of the wash cycle is a mixture of debris, dirt, grease and microfibers and potentially large objects such as coins or nails left in the clothing. This effluent is then drained and pumped out of the drum at a typical rate of 3-8 gallons per minute. Second or third rinse cycles with clean water may be performed, resulting in effluent with less concentrated contaminants. The drain rate of the washing machine is impacted by the level of water in the drum, the height of the outlet point and if a filter is connected to the outlet.
In a typical wash, the highest concentration of microfibers is in the range 5 mm to 50 μm but shorter microfibers exist that are still harmful in the environment. If it were required to remove 99% of microfibers of all sizes down to 50 μm in length, a mesh with apertures of 25 μm would theoretically be able to achieve this. In practice however, such a mesh placed directly in the stream of effluent will clog almost immediately and the filter will become inoperable. This will create a rise in pressure consumption in the outlet and potentially damage the pump.
A conventional separator or filter arrangement is shown in
Curve 1 in
In practice, the flow of effluent from a washing machine is not constant over time because a limited amount of water is used in each wash cycle. Curve 2 in
To operate a filter at its optimum level requires the pressure to be regenerated when required. It is an object of the invention to solve the problem of optimising the pressure regeneration process.
In an embodiment, a separator for separating solid material from a fluid is provided, the separator comprising: a chamber with an inlet and an outlet, a sieve structure forming a permeable barrier between the inlet and the outlet to filter the fluid, the sieve structure thus having an inlet side for unfiltered fluid and an outlet side for filtered fluid,
The sensor may be located at the inlet or at the outlet.
The pressure sensor may detect pressure from the inlet to the outlet to determine pressure across the separator.
A reservoir may be provided below the chamber and the sensor may be located in the reservoir. The sensor may also be located at the conduit that feeds the inlet to the filter, the outlet to the filter or where a bypass conduit may be located.
Some detector types, such as a pressure differential sensor may use multiple locations to provide differential measurements whereas others may only require a single location.
The reservoir may have a main outlet and a drain outlet for draining the reservoir below the main outlet and wherein the fluid detector is located in proximity to the drain outlet.
The sensor may be a fluid detector such as a float switch or a capacitative sensor. The sensor may be a pressure sensor for sensing the pressure differential between the unfiltered and filtered sides of the sieve structure.
The chamber may be cylindrical and the sieve structure may be a coaxial cylinder within the chamber and wherein a wall may be provide to one side of the inlet such that the fluid is guided around the sieve structure through a channel such that filtered solids dislodged by cleaning fluid from the cleaning nozzle accumulates on the side of the wall away from the inlet. The advantage of this arrangement, whereby filtered solid materials progress along a channel, is the better use of space, increased solid material collection capacity and ease of handling filtered solids.
A trap may be provided comprising an opening in the base of the channel to a sub-chamber, where the accumulating filtered solids can be collected.
The nozzle assembly may comprise a plurality of cleaning nozzles that are rotatable around the central axis of the sieve structure.
The nozzle assembly may be rotated by propulsion nozzles arranged to direct a stream of water. The nozzles may be arranged off-centre from the central axis to provide propulsion or have a vector that is offset from the central axis or is tangential to the circumference of the sieve structure.
The chamber may have a closed top and bottom.
The sieve structure may have an opening at the top to relieve pressure.
The pump may be a water pump arranged to drain the separator.
The pump may be arranged to recirculate the filtered fluid to the conduit of the filter pressure regeneration apparatus and/or drain the separator.
A second pump may be arranged to recirculate the filtered fluid to the conduit of the filter pressure regeneration apparatus.
The separator further may comprise an air pump located between the pump and the filter pressure regeneration apparatus to introduce air into the conduit and to drain the separator.
A bypass conduit may be provided between the inlet and the outlet to provide an alternative route for fluid in the event that the flow of fluid is impeded. The bypass system may include an electronically operated valve.
A diverter valve may be provided to recirculate the filtered fluid to the conduit of the filter pressure regeneration apparatus and/or drain the separator.
The nozzle assembly may comprise a nozzle arranged to direct a stream of fluid towards a rotatable plate, wherein the plate is arranged to rotate under the force of the stream of fluid and to project the fluid outwards towards the sieve structure.
In an embodiment, a method of operating a separator of the type described above is provided comprising the steps of; filtering an fluid through a sieve structure, detecting at least one state of the separator and performing an operation in dependence on the detected state of the separator.
The state of the separator may include the presence or level of fluid in the separator.
The state of the separator may include the pressure differential between the filtered side and the unfiltered side of the sieve structure.
The operation may include operating a drain pump.
The operation may include operating a pressure regeneration apparatus that is arranged to spray the filtered side of the sieve structure with wash fluid to dislodge debris from the unfiltered side of the sieve structure.
The operation may include operating a recirculation pump to recirculate a portion of the filtered fluid to the pressure regeneration apparatus.
The operation may include operating a bypass system that includes an electronic valve.
The operation may include operating a diverter valve to recirculate filtered fluid to the pressure regeneration apparatus or direct water to drain.
While the description that follows focuses on washing machines for clothes, it is to be understood that the teachings herein are not limited to use in washing machines as they are equally suited to other processing appliances, such as but not limited to driers, such as wash-dryer combination machines, tumble driers, dyeing machines, cutting machines, recycling machines, dry cleaning machines and so on. The washing machines or other processing appliances could be domestic or commercial. The teachings herein could also be used in other industries in which microparticles may be generated as a result of processing of items. References to washing machines herein are therefore to be understood as comprising any similar appliance of the types contemplated herein.
The separator described herein may be installed within the appliance itself during manufacture as shown in
The separator system 1600 described above may be installed within a washing machine, as shown in
It will further be appreciated that the teachings herein are suited to any application, which requires the removal of microplastics, including microfibers, from any effluent, including wastewater, within which such materials may be entrained.
It should be noted that wastewater from a washing machine, and other applications, contain a wide variety of compounds including microplastics. Although the filter is specifically suited to the capture of microplastic, due to the environment in which it operates, this system is also robust against the harsh and varied compounds the filter comes into contact with and is also suited to filtering out any solid material entrained in an effluent.
Effluent is understood to include wastewater from the sources mentioned above. It can also include the wastewater from Wastewater Treatment Plants. Effluent includes entrained dirt, detergent and micropollutants including microplastics, which include microfibers.
The fluid sensor could be arranged so that it is activated when a particular level of fluid is detected and then activates either the drainage of the separator or pressure regeneration apparatus or both. Alternatively, the fluid sensor could be graduated so that it determines the level of fluid in the reservoir and the drainage is activated at a given level and the regeneration is activated at a different fluid level.
The separator unit is around 15 cm in diameter. However, it will be appreciated that larger or smaller diameters could be selected depending on the application. The size of the unit is selected on the flow rate of effluent to be filtered. A separator diameter of 15 cm is sufficient to process the effluent from a domestic washing machine flowing at a rate of 10 litres per minute.
The open area of the mesh that enables the passage of water at a given flowrate can be adjusted by changing either the surface area of the mesh or the mesh aperture. The mesh aperture effects the efficiency, so a smaller mesh aperture is generally preferable to provide greater efficiency. The mesh surface area is a function of the height and diameter, therefore a given area can be matched by increasing the height if the diameter is reduced, and visa versa. All variables can be adjusted to meet product packaging and efficiency specification requirements.
The separator has a filter pressure regeneration system comprising a nozzle assembly that has a central hub 611 supporting one or more cleaning nozzles 612a, b etc that extend radially from the hub 611. The hub includes a conduit to feed pressurised wash fluid to the cleaning nozzles. The cleaning nozzles are arranged as a stack of four directly above each other and a matching stack directly opposite on the hub. This arrangement ensures that the entire width of the sieve structure is cleaned in each sweep of the nozzle assembly. The central conduit 612 feeds the cleaning nozzles with pressurised wash fluid, in this embodiment the wash fluid is mains water controlled by a solenoid valve 615. Effluent enters the separator via inlet 603 and passes around the channel formed by the outer wall of the chamber and the sieve structure 604 around to the wall 605 where filtered material accumulates in the trap 606. The cleaning nozzles 612a, b are aligned perpendicularly to the sieve structure 607. A nozzle assembly rotator that is fixed to the cleaning nozzles rotates the cleaning nozzles. The nozzle assembly rotator 613 comprises a central hub 614 that acts as a conduit for propulsion fluid. The wash fluid conduit and rotation unit hub are connected so that the wash fluid propels the nozzle assembly. The rotator 613 has radially extending arms that terminate in propulsion nozzles that are directed perpendicularly to the arms. Fluid exiting the propulsion nozzles is directed tangentially to the axis of the hub, causing the nozzle assembly to rotate.
An alternative arrangement is shown in
It may be advantageous to be able to control the drainage of a separator unit and the pressure regeneration separately.
A reservoir 911 with a fluid sensor such as a float switch 912 is provided beneath the separator unit. The fluid sensor detects when fluid is present in the reservoir. It can be arranged to determine the level of fluid in the reservoir. The fluid sensor is arranged to control the recirculation pump 908 to wash the sieve structure to regenerate the filter pressure and/or the drainage pump 905. Alternatively a sensor can be provided at the inlet to detect when fluid has entered the system or if effluent is backing up and this can be used to activate the pump to regenerate the filter pressure. A pressure differential sensor could be provided to detect when there is a difference in pressure between the inlet and the outlet and pressure regeneration is required. The drainage pump could be operated when fluid is detected in the reservoir or when a particular level of fluid is detected or when any fluid is detected anywhere in the system.
A bypass system 1000 may be provided to connect the inlet 1001 to the outlet 1002, as shown in
An embodiment of a separator unit has a bypass feature for allowing effluent to go around the filter if it becomes clogged. The separator unit has an effluent inlet, a housing supporting a sieve structure and an outlet. A bypass conduit links the inlet to the outlet. A pressure-activated valve is located in the conduit. The pressure-activated valve opens when the pressure at the inlet exceeds a certain pre-set value. Therefore, if effluent backs up at the inlet because the filter is clogged, the valve will open and let effluent through to the outlet where it can safely discharge to a waste pipe. Alternatively, the valve may be of a type that can be electronically controlled. A pressure sensor that detects a pressure differential between the two sides of the sieve structure can control the valve, so that if the pressure differential reaches a predetermined level, the valve is operated and the bypass activated.
The separator system 1600 described above may be installed within a washing machine, as shown in
A separator unit for locating externally to a textile processing apparatus such as a domestic washing machine is shown in
Located within the filter assembly of the jug is a pressure consumption regeneration apparatus comprising a rotatable nozzle assembly 1210 mounted on a hollow spigot 1211. The rotatable nozzle assembly is captive on the spigot by the filter assembly cap 1203b. The spigot is fed by a conduit that is routed through the unit to a recirculating pump 1216a, shown in
The jug 1203 is provided with a moulding 1212 that collects the filtered effluent that has passed through the mesh. This moulding channels effluent to the jug outlet 1213. The jug outlet feeds two reservoirs; a recirculation reservoir 1214 and a drainage reservoir 1215. The recirculation reservoir is connected to the recirculation pump 1216a. The drainage reservoir is connected to a drainage pump 1216b, shown in
Upon drainage from the filter unit the reservoirs are arranged to prioritise filling of the recirculation reservoir before the drainage reservoir. This ensures that there is always a supply of wash fluid for recirculation and it is not removed by the drainage pump.
The volume of the recirculation reservoir is designed to ensure a supply of wash fluid that can provide constant recirculation without fully emptying the reservoir. It might be advantageous in some scenarios to limit this and only provide enough wash fluid for a ‘burst’ as the reduction in this volume enables the product size to be reduced.
The volume of the drainage reservoir is designed to ensure any back flowing fluid from the outlet ducting and hose pipe can back fill into this chamber without overflowing. This ensures that the user can remove the filter jug when the product is installed close to the floor level and not result in any flooding.
The geometry of the reservoirs is designed with an angled base and centralised feed point for the pumps. This reduces sedimentation in the tank by removing static flow areas in the tank and creating a dynamic drainage environment that encourages particles to travel to the feed point and be removed by the pump along with any waste water.
The geometry and depth of the reservoirs is further designed to limit vortexing of the pumps which would otherwise reduce their ability to draw water into the pump and reduce their operational efficiency
The inlet 1201 and outlet 1219 of the unit 1100 are connected by a conduit 1220. A dispensing valve, 1221 is provided at the entrance to the conduit 1220. The dispensing valve opens at a predetermined pressure, so that if there is a fault in the unit and pressure builds up, the valve operates and effluent bypasses the filter section of the unit straight to the outlet. One-way valve 1222 is provided to prevent filtered effluent re-circulating and one-way valve 1223 is provided to prevent by-passing effluent to enter the reservoirs. In another embodiment of the design, the user can gain access to the bypass for maintenance, for example to remove a blockage.
An air valve 1224 is provided in the inlet to prevent the recirculation pump and/or the drainage pumps from drawing water out of a connected washing machine, to ensure that there is sufficient water left in the washing machine.
The capacitive sensor is a type of fluid sensor; any other type could be used, such as a float switch. A suitable capacitative sensor is XKC-Y25-NPN by True Sense®. A suitable pressure sensor is a ABPDRRV001PDSA3 by Honeywell.
The electronic system is arranged to operate the unit in numerous modes involving different combinations of sensors and software logic, to optimise the system operation or vary it for differing regional, user, functional or cost requirements. For example, only a capacitive sensor could be used (no pressure sensor) to reduce the number of components and cost. The following are examples of modes of use:
If the capacitive sensor indicates that there is effluent present at the inlet (i.e. that the washing machine is emptying) and the pressure sensor indicates that the mesh has blinded over, then the drainage pump is activated to drain the unit and the recirculation pump is activated to spray the mesh to remove the debris and regenerate the pressure consumption. Active filtering may run for a set time once it has been triggered.
If the pressure sensor indicates that the pressure differential is below a threshold and the capacitive sensor is triggered, then passive filtering is initiated. This is where the recirculation pump is turned off and only the drainage pump is operated.
If the capacitive sensor indicates that effluent at the input has ceased, then the recirculation pump is operated after a delay, which could be around 100 seconds, to clean the mesh; this delay can be adjusted. Shortly after, for example 2 seconds, the drainage pump is operated to drain the system. The recirculation pump is then turned off after, for example, a further 3 seconds and then the drainage pump is turned off after, for example, 10 seconds. If the capacitive sensor detects input effluent then the drainage cycle is interrupted and the filtering mode is initiated again.
If the capacitive sensor is low, then the recirculation and drain pump are both turned off.
The capacitive sensor is provided on the inlet pipe. When water is detected the pumps are activated until water is not detected anymore. The pumps are programmed to overrun by a predetermined number of seconds to clean the mesh and drain the filter.
The capacitive sensor is provided on the inlet pipe. When water is detected, the drain pump is turned on. If current on the drain pump is low while the fluid sensor is reading high, then the recirculation pump is turned on. The recirculation pump is turned off after a predetermined time while the drain pump is left on.
The separator unit may be integrated into a washing machine or other textile processing apparatus. No fluid sensor is required as integration with the washing machine control logic enables the filter to know when water is being pumped into the filter. When fluid is pumped through the filter and the pressure sensor is low, the recirculation pump is not run, but the drain pump is activated. When fluid is being pumped through the filter and the pressure sensor is triggered, then the recirculation pump is run. The washing machine drain cycle can be paused at this point for a few seconds to increase the pressure consumption regeneration effectiveness.
The unit may be used to reduce the water consumption of an existing washing machine or other textile processing equipment, by recirculating the water from the output back into the washing machine. This is possible because the filter removes a high proportion of the debris from the effluent and is therefore very clean. A unit that is integrated into a washing machine could provide this functionality too.
The separator unit could be integrated into a washing machine and used to replace the conventional filter that is used to prevent debris from reaching and damaging the washing machine pump. Furthermore, by replacing an existing filter with the advanced filtering technology disclosed herein, a different washing machine pump could be used altogether, one that operates at a higher efficiency.
The pressure sensor may be monitored in a predictive manor to enable software to pre-empt when the filter is reaching saturation point and activate the regeneration before this time.
The pressure sensor may be monitored by the software to predict how much material the filter has captured and if the user should empty it. Additionally, by monitoring the pressure sensor data the bypass state can be determined. This information can then be displayed to the user. In an embodiment this might be through the interface on a retrofit filter or the user interface display of the washing machine.
In an embodiment where the filter is in communication with the washing machine the pressure sensor and the capacitive sensor may be omitted and the regen run based on timed intervals or other logic. It may be beneficial to start and stop the washing machine drain cycle during regeneration bursts to maximise the mesh cleaning power of the jets.
A separator may be provided where the inlet feeds the interior of the sieve structure and the outlet collects filtered effluent from the outside of the sieve structure.
The separator housing may be opened to empty the trap when the effluent has been drained.
An opening at the top of the sieve structure may be provided to avoid air locks.
An air inlet may be provided at the inlet of the separator to avoid syphoning all of the waste water out of a washing machine.
As an alternative to regenerating the pressure of the separator unit, a disposable cartridge may be provided. The part of the separator that contains the filtering element, i.e. the sieve structure, could be provided as a cartridge, that is removed and disposed of and replaced with a new one. Alternatively, the cartridge could be sent for cleaning and then re-used.
Wastewater expelled from textile factories is contaminated with microfibres and it is not guaranteed it will be filtered at municipal facilities. When these facilities exist, they may remove up to 98% of microplastics, however what escapes still equates to millions of microfibres every day. Microfibres removed from water may then be passed to the environment as “sewage sludge”, spread on agricultural land as fertiliser. Ultimately microfibres are passed as pollutants into the natural environment—they need to be stopped at source.
Wet-processing factories currently operate in a linear system, whereby microfibre resources are expelled as pollutants from the technical process into the biological environment. Use of the separator system described herein closes the loop into a continued cycle to retain the value of the microfibres within the technical process and stop damage to the biological environment.
An embodiment of the separator system can be retrofitted onto the existing wastewater outlet of wet-processing textile factories to enable microfibre capture at source before pollution of the natural environment can occur.
The separator system can be used to filter microplastics and other micropollutants from environmental drainage systems, such as roadside gullies. A lot of microplastics in the environment break down from larger items of plastic such as car tyres, road surfaces and road markings. After synthetic textiles, tyres are the largest source of microplastics and contain harmful materials such as mineral oils.
Catalytic converters are fitted on most cars and contain highly valuable materials such as platinum, palladium, copper and zinc. During use, small amounts of these metals are lost from cars and fragments are deposited on the road surface. While metal concentrations vary geographically, collection and recycling of these materials not only reduces environmental pollution but can also be a revenue stream in a circular economy.
A larger-scale embodiment of the invention can be applied to the treatment of effluent in Wastewater Treatment Plants. For example, the chamber of the separator could be 1 meter in diameter or 2 meters or greater.
Typical sewage networks are built along one of two designs:
In both systems, roadside runoff, i.e. surface water from the roads, is released into the environment.
Most roadside gullies have drains located at regular points and these drains have a sediment “pot”, which lets heavy materials like gravel and sand settle to prevent blockage. These hold some micropollutants, but the majority of microplastics and valuable metals are too small and are not retained.
An embodiment of the separation system of the present invention can be retrofitted as an insert into the sediment pot of a drain to filter micropollutants at source. It is designed to fit existing gullies and to be emptied using a mobile vacuum pump.
The disclosure in the abstract is incorporated herein by reference.
In another embodiment the system can be used as part of a filtration system for maritime waste disposal. At sea shipping vessels dump wastewater contaminated from activities on the ship, which include microplastic from various sources. The filter system can be applied to filter this effluent prior to disposal and thus combat this pollution source.
Number | Date | Country | Kind |
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2106277.3 | Apr 2021 | GB | national |
2116312.6 | Nov 2021 | GB | national |
Filing Document | Filing Date | Country | Kind |
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PCT/EP22/61492 | 4/29/2022 | WO |