The invention concerns a method for cleaning a water environment of sludge and a device for cleaning a water environment of sludge, in particular an aquarium, miniature decorative pond, or oceanarium.
Known methods of cleaning a water environment base upon an idea of straining out impurities from water with strainers or filtering beds formed from sponge or other materials, like synthetic non-woven fabrics or activated carbon; or base upon the floatation idea, that is removing impurities together with foam resulting from entering and diffusing air or another gas into water.
Filters located internally or externally in relation to the tank or basin of the water environment cleaned are used for methods based upon straining out. Filters arrest and collect mechanical parts occurring in water, like sludge, small fish, snails, life feed intentionally released into the environment, and plankton desirable in the environment. Often a filtration bed constitutes a desirable biochemical microbiological activity carrier, transforming onerous impurities (physical or chemical) dissolved in water into harmless or less onerous substances.
Foam skimmers are used for floatation methods. Thanks to foam forming, separating and carrying away, occurring in these devices, they remove main hydrophobic components from the environment cleaned. Hydrophobic components show affinity to the water-gas boundary surface. There are mainly high-molecular soluble substances like waste proteins and microorganisms, in particular bacteria.
Patent description GB 727459 presents a device for removing sludge from the bottom of an aquarium tank. It strains out water-borne objects from water, forcing passage of water through a filtration bag made of a water permeable fabric. The bag arrests sludge and living organisms borne by the water stream. At the bottom the bag is attached to a vertical pipe performing the mechanical, load-bearing and connecting function for the filtration bag and the water driving unit. The water driving unit consists of a vertical pipe. A compressed air tube has its outlet in this pipe. Under the air tube outlet the vertical pipe extends towards the tank bottom, where its intake sucks water in, together with impurities and living organisms, which should stay in the environment. Sludge along with living organisms is sucked in through the pipe inlet and falls into the filtration bag, and the living organisms are trapped in the filtration bag. The bottom end of the filtration bag is closed with a stiff clip.
The sludge arrested in filters causes their blocking and clogging, which entails the need for frequent labour-intensive replacements or regenerations (e.g. by laundering, rinsing in separate appliances) of strainers or filter beds. The sludge arrested in a filter still has an impact on the environment as the water passing through the filter is in a constant contact with this sludge. The effect of arresting in the filter of such objects as small fish and snails or intentionally released feed for animals living in the environment cleaned is disastrous as it often causes degeneration of creatures trapped in the water environment. Usefulness of foam skimmers for sludge removal from the water environment cleaned is insignificant.
As it is impossible to remove sludge by filters and foam skimmers with adequate efficiency, maintaining a sludge free condition of an environment requires a separate labour-intensive care, consisting in manual cleaning of sludge from the bottom with an appliance sucking in water, which is a water equivalent to vacuum cleaning.
The objective of the invention is to enable efficient removal of sludge from a water environment at a small effort and at the same time to save biotical environment components, such as small fish, snails, plankton or live feed added to water. In other words the objective is to remove sludge in a maintenance free, automatic and non-invasive manner. The objective of the invention is also to develop a device for a non-invasive method of cleaning a water environment of sludge.
The essence of the method of cleaning a water environment of sludge consists in feeding water with sludge above and/or to the upper zone of a chamber, where it flows through and off from above the stagnation zone, where stagnation of the water and sludge mixture is maintained, and in these circumstances the sludge gravitates towards the chamber bottom, where it is periodically or continuously removed from. The flow of water with sludge in the near-surface upper layer is disturbed to the depth from 1 to 1,000 mm depending on the stagnation zone depth, advantageously to 10 mm.
The essence of the device according to the invention is at least one supply channel, which has an outlet in the upper zone of the chamber and the outlet bore is located in this upper zone. The chamber with impervious walls in its lower part is a sludge container. At least one supply channel and/or its outlet is located inside the chamber and/or tangentially to the chamber wall. At least one chamber wall has a mirror layer on its surface. The sludge container may be a separable part of the chamber. The chamber extends downwards from the upper zone and the half of the total wall area is at least a few times larger than the horizontal cross-section area in the upper zone of the chamber.
The device along with the chamber and the supply channel constitutes and integral part of an aquarium. In an embodiment variant the device along with the chamber and the supply channel constitutes a replaceable module placed in an aquarium.
In the invention development the chamber is divided into compartments set by vertical partitions. In an advantageous embodiment partitions are parallel. The length of partitions may vary. The upper ends of partitions of various lengths in at least one compartment layer set at least one inclined plane situated askew in relation to the aquarium side walls, in addition the water outlet bore is located in a side of the chamber.
In an embodiment variety two inclined planes are situated in the V-form, and the water outlet bore is located in a side of the chamber.
The chamber has a mesh in its upper zone. The mesh may be removable.
The driving module is made in the form of a supply channel section, on its inlet a gas distribution member is located, advantageously air or oxygen, with a perforated or porous coating advantageously on the chamber's length. In the variant the driving module is made in the form of a supply pipe section connected to a magnetohydrodynamic pump or being a part of the pump. The driving module in the form of a magnetohydrodynamic pump is mounted on the chamber outlet side. The device is additionally connected to its mount in a separable manner and is accommodated in a contour similar to a sphere, cubicoid, cylinder or pyramid.
An advantageous effect of the method is the solution to the problem of cleaning of sludge a water environment, in particular a decorative miniature pond, aquarium or oceanarium, in a non-invasive manner. Non-invasiveness in this case means lack of destruction and reduction in losses of desirable biotic components of the environment, such as small animals, desirable plankton suspended in water and others. It is fundamental particularly for marine fish keeping or animal breeding in oceanaria, as keeping plankton eating animals in captivity is difficult or even impossible, as water needs to be cleaned of sludge by filters with a side-effect of catching biotic components suspended in water by the same filters. Meanwhile, filter feeders are indeed the main dissimilarity and attraction of marine environments. They are plankton eating animals, like sponges, jelly-fish, whale sharks etc. So far they have been beyond the reach of breeding techniques, or breeding of some of them has been possible, albeit difficult.
An advantageous effect of the device according to the invention is its simple design, enabling a stable operation of the cleaning process of a water environment of sludge.
The invention is presented in a picture, where
FIG. 2—shows a schematically presented device for cleaning a water environment of sludge with the driving module at a channel inlet,
FIG. 3—shows a diagram of the device with the driving module sucking in the water stream,
FIG. 4—shows a diagram of the device with a gas distribution member downstream the supply channel inlet,
FIG. 5—shows the application of a wall with a mirror-layer in the device,
FIG. 6—a cross-section through an oblong rectangular aquarium with the device located next to a wall,
FIGS. 7 and 8—directions of water flows caused by the application of the device in an aquarium,
FIGS. 9 and 10—show the device with a back channel and a water flow diagram if the device is located in an aquarium corner, in a top and a side view,
FIGS. 11 and 12—show the device with side channels, located in an aquarium corner, in a top and a front view,
FIGS. 13 and 14—show the free standing device with an axial channel, in a top and a side view,
FIGS. 15 and 16—show the free standing device with the channel on a perimeter part, in a top and a side view,
FIG. 17—shows the device with a removable concentrated sludge container,
FIG. 18—shows a diagram of the device with water stream flow forced by a magnetohydrodynamic drive,
FIG. 19—shows a schematically presented device for cleaning a water environment of sludge with the chamber and the supply channel, in the basic variant,
FIG. 20—the device with the chamber divided into compartments in a perspective view, as a replaceable module,
FIG. 21—an aquarium with a separate integral part for the device, in a perspective view,
FIG. 22—the device constituting an integral aquarium part, in a top view,
FIG. 23—the device constituting an integral aquarium part, in a side view,
The method of cleaning a water environment, in particular an aquarium or oceanarium, of sludge consists in intaking a concentrated stream 51 of water bearing sludge 6 and supplying it to the chamber 1. Water with sludge 6 is supplied above and/or to the upper zone 13 of the chamber 1, which in its lower part is a concentrated sludge 61 container 11. In the upper zone 13 water flows from the concentrated stream 51 direction and flows out with the outgoing stream 52 from above the stagnation zone 15. The lowest layer of water flowing over the stagnation zone 15 only slightly disturbs the stagnation of the mixture of water with sludge particles 601. In these circumstances sludge 601 gravitates towards the lower 14 zone of the chamber 1. The concentrated sludge 61 is removed from the chamber 1 bottom periodically or continuously. To remove foamed bacteria and waste proteins in the foam 42 floating on the surface, the flow of water with sludge 601 particles in the near-surface upper layer is disturbed with a disturbing barrier 41 to the depth from 1 to 1,000 mm from the set water level 58 depending on the depth of the stagnation zone 15. Fish 72 and other creatures, e.g. snails 74, 75 may freely get into the chamber and leave it without any fear of being trapped.
The device made according to the invention has a chamber 1 connected to at least one supply channel 3, moreover at least one supply channel 3 has an outlet in the upper zone 13 of the chamber 1. In this upper zone 13 there is also an outlet 301. In its lower part the chamber 1 with impervious walls 12 is a concentrated sludge 61 container 11. The chamber 1 is extended downwards from the upper zone 13 and the half of the total wall 12 area is at least a few times larger than the horizontal cross-section B area in the upper zone 13 of the chamber 1.
The device along with the chamber 1 and the supply channel 3 may be a replaceable module placed in an aquarium (
The chamber 1 is divided into compartments 120 set by vertical partitions 121. The partitions 121 are parallel to each other.
The partitions 121 may also have the form of flat bands or may have any shapes. In the cross-section the partitions 121 may outline a contour of any geometrical figures.
In an embodiment variant the partitions 121 have various lengths and in at least one layer of compartments 121 their upper ends outline an inclined plane 122 located askew in relation to the aquarium side walls 59. In such a case the water outlet 301, through which the stream 52 flows, is situated in a side of the chamber 1.
In another embodiment two inclined planes 122 are form a V-shape, and the water outlet 301 is located in a side of the chamber 1. The chamber 1 has a mesh 123 in its upper zone. The mesh may be removable.
Implementation of division of the chamber into compartments set by vertical partitions prevents fish and other inhabitants of the aquarium from getting inside the chamber. The chamber constitutes a stagnation zone, therefore a presence of any aquarium inhabitants would cause sludge dispersion. The mesh situated in the upper zone of the chamber performs an identical role.
The driving module 2 is located in the inlet 361 zone of the supply channel 3, advantageously on the whole length of the chamber 1. The supply channel 3 is connected to the driving module 2 or is the driving module 2. The driving module 2 in its simplest form is a section of the pipe 28 supplying gas with a distribution member 21 in the form of a perforated and/or porous water permeable coating. In the embodiment for higher water flow efficiencies the driving module 2 is a magnetohydrodynamic pump 23. In an embodiment variant the driving module 2 in the form of a magnetohydrodynamic pump 23 is connected at the outlet 32 of the outlet channel 31 of the chamber 1.
In general, the best method of forcing water movement in the device is to use a driving module 2 with lifting gas in a restricted space, as shown in
In a system of this kind, water with gas bubbles 22, as having a lower specific gravity than pure water, because of the buoyant force exerted by water beyond the pipe, is lifted up and thus the flow of this water through the upper part of the chamber 1 is forced.
The sludge resting 62 on the bottom 57 is drawn into the supply channel 3 in the same direction as the incoming stream 511.
Above the water level 58, bubbles 22 flowing out to the surface form foam 42, which not only should be isolated from the rest of the environment cleaned, but seized and disposed outside, which very advantageously results in the foam skimmer function performed by the device. To this end, water flowing through the chamber 1 in its upper zone 13 is disturbed with a disturbing barrier 41, which causes gathering of foam 42 and enables to discharge the foam outside of the system.
In addition, the driving module 2 utilizing gas for lifting the water stream enables the device to perform the function of aeration, oxidizing or enriching water in carbon dioxide. Intensity of these functions may be very desirable. It is vital that the invention performs these functions reliably.
The lifting water with gas efficiency of the driving module 2 depends monotonously on the difference between the height of the cross-section bore through which water flows into the driving module and the lower edge of the bore through which water leaves the unit flowing into the chamber 1.
For optical isolation of the dark bed of gathered sludge, on the water environment 5 side the walls 12 of the chamber 1 have features of a mirror surface, as shown in
The general pattern of water circulation, caused by the device operating in the water environment cleaned, is very important for the hydrodynamics of the environment cleaning. No water stagnation zones should occur in a well maintained water environment. The only such a zone should be the interior of the chamber 1 gathering sludge particles 601. In addition, there should be a tendency to carry sludge particles 601 suspended in water by water movements, possibly with a contribution of gravitation, towards the inlet 361 of the channel 3 supplying water to the chamber 1. Therefore location of this inlet 361, as well as the presence of an outlet channel 31, offtaking water from the upper zone 13 of the chamber 1 to some selected place of discharging it to the environment, as well as possible presence of directing members 35 the stream of outflowing water—depend on the shape of the tank or basin of the water environment 5 cleaned, and its nature, for example in the sense of a presence or lack of floating plants 79 canopy on the water surface.
The device solution to be applied in a classic aquarium is illustrated in
Another solution of the device to be applied in a classic aquarium is illustrated in
Another solution of the device may be applied mainly in a square base aquarium. The structure 102, of a triangular vertical projection, occupies a tank corner, particularly in an aquarium like the one shown in
At the top water pours into the chamber 1, which has a trapezoidal horizontal cross-section, in the same direction as the concentrated stream 51, which leaves the chamber 1 through an outlet channel 31 with a directing member 37, which directs the stream horizontally tangentially to the wall 59 in the upper zone of the tank, in particular an aquarium. The operation of the device generates a slow water eddy throughout the whole tank (in the vertical projection) designated as 552 and favouring detaching of the resting sludge 62 from the bottom. The eddy causes lifting of the swirling sludge 65 in the bottom zone of the water tank (aquarium) and moving it towards the water intake 33 located near the tank centre, in the same direction as the water bottom stream 53.
Another solution of the device may be used in a classic aquarium with the water surface occupied by plants freely floating 79 on the surface. The chamber structure 102, of a triangular vertical projection, occupies a corner of the aquarium with walls 59, as shown in
The supply channel 3, designated in the vertical projection as 302, occupies the triangular corner of the acute corner of the whole structure 102 including the tank 102, which is triangular in the vertical projection, whereas the outlet channel 31, designated in the top projection as 312, occupies the triangular acute corner of the device structure on the opposite side. Under the inlet gap 36 into the vertical channel 302 supplying water into the structure 102, the gas, in particular air, distribution member 21 rests on the substrate 571. The sludge taken out 66 supplied with the supply channel 3 gravitates to the chamber 1 in the settling direction 67. At the top, water leaving the structure 102 flows in with the outgoing stream 52 into the outlet channel 312, adjacent to the structure 102 on the opposite side as the channel 302 supplying and driving water.
The outlet channel 31 leads water downwards with the outgoing stream 52, and in the bottom zone it releases water through the outlet gap to the aquarium water environment 5 in the same direction as the bottom stream 53. The bottom stream 53 is directed horizontally tangentially to the tank wall. The operation of the device generates a slow water eddy throughout the whole tank in the same direction as the lifting stream 551. This eddy so to speak spreads the sludge 6 to corners, in particular driving it to the corner with the inlet gap 36 of the channel 3 supplying water to the chamber 1. Water in the eddy raises at the tank walls and in the upper zone, in the same direction as the rotation stream 791, advantageously pushes the floating plant 79 raft away from the tank walls 59, making possible and setting the plant agglomeration in slow and very advantageous rotary motion.
Another solution of the centrally located device to be applied in an aquarium of a spherical or cylindrical shape is presented in
The chamber 1 designated in the vertical projection as 102, surrounds the supply channel 3 or in the projection onto the mount plane it has a shape of a sickle tangential to the supply channel 3, as shown in
A solution of the device to be applied in marine aquaria simulating conditions in the intertidal zone may be derived from any of the versions discussed earlier. In this case it is important: the height of characteristic elements of the device structure above the cleaned water environment 5 bottom 57, namely the threshold or bottom of water overflow from the supply channel 3 to the chamber 1, the threshold or bottom of water outlet from the chamber 1, the upper limit of the water outlet bore from the chamber 1, which must always remain under the water level 58 to prevent foam 42 release, must be adjusted to the assumed minimum water level 58. Lowering of the height of location of the mentioned elements governing the water flow through the device results in a reduction of water flow efficiency, in particular of concentrated sludge 61 container 11 capacity. The solution takes into account the change in the environment cleaning hydrodynamics, from hydrodynamics typical to the basic version of the device, applicable for a low water level, to untypical disturbed hydrodynamics for a high water level.
The device to be applied in miniature decorative ponds is illustrated in
A deep-water aquarium is a water environment in the meaning of this solution, maintained in condition of high hydrostatic pressure, as prevails in sea at a depth of 100 m. At present the deep-sea animal breeding technique is becoming more common, due to scientific motives, and recently also due to commercial reasons. It is a very specific technique. For instance, interesting and at present already bred species, like phylogenetically ancient shell cephalopod nautilus (genera Nautilus and Allonautilus at present bred only in captivity), do not grow correctly not only when the pressure is normal, but also when the gas content in water, including even inert gases like nitrogen, is increased. It excludes any solutions with the presence of dissolved gaseous phase in the cleaned high-pressure water environment.
A solution according to the invention adapted to the high-pressure water environment requirements is presented in
The driving module 3 may also be a part of the outlet channel 31 offtaking water from the chamber 1 of the device to the cleaned environment. The specificity of the magnetohydrodynamic drive requires that the drive section of the water supply channel 3 have the form of a tube of a ring cross-section, or in other words, a tube with a tube inside, where water bearing sludge taken out 66 by the incoming stream 511 flows between the tube walls. The internal tube limits the empty space, or a space accommodating the ferromagnetic core 25 of the power unit. Also from the outside the coil 24 is then equipped with a ferromagnetic element 26, improving magnetic circuit properties. Due to the pressure, the chamber 1 is cylindrical with a bottom outlet for the tube offtaking the concentrated sludge 61, on which the valve 381 is installed. The water supply channel 3 surrounds the chamber 1 and has the outlet to the chamber 1 as a slot on the perimeter of the upper end of the chamber 1 enabling gravitating of the sludge 6 in the settling direction 67. Water cleaned of the concentrated sludge 61 is returned to the water environment 5 limited with walls 59 through the outlet channel 31 in the same direction as the outgoing stream 52.
The driving module 2 coils 24 are supplied with an alternating current of various phase angles for each of the coils 24, so that in a given time interval the coil 24 activity shifts from the bottom to the top and thus moves water molecules upwards. The phase of each of the coils 24 is presented visually in graphs 242 separate for each of the coils 24. The chamber 1 becomes an equivalent of an internal pipe, giving to the stream of driven water the desirable shape of a hollow cylinder. In turn, the central ferromagnetic core 25 of the magnetohydrodynamic pump 23 fills the chamber 1 walls and closes lines of the electromagnetic field 241.
In the embodiment variant the driving module 2 in the form of a magnetohydrodynamic pump 23 is mounted on the chamber 1 outlet side.
If the described solutions according to the invention are applied, a drastic reduction in labour intensity of operation and maintenance or commonly known kinds of water environments is obtained. In addition, breeding of creatures so far impossible or extremely difficult to breed due to their dependence on plankton feeding, like marine jelly fish in amateur aquaria, shark fish in oceanaria, clams in ordinary home fish tanks becomes possible at all or is made much easier. Moreover, it is also possible to maintain high ecological quality of artificial water environments, of which small organisms staying in water depths are a significant biotic component. Also a commercial activity, such as fish breeding and fry raising can be improved very much.
Number | Date | Country | Kind |
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P 385 891 | Aug 2008 | PL | national |
P 388 573 | Jul 2009 | PL | national |
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/PL09/50022 | 8/18/2009 | WO | 00 | 5/6/2011 |