This invention relates to a method for the removal of sludge and/or sand from the bottom of a wetland.
The invention applies both to the removal of sludge and to the removal of an underlying sand layer up to a certain depth. For the sake of simplicity, the term sludge is used below, which also refers to the underlying sand layers.
More specifically, the method relates to the in situ pumping up of polluted sludge underwater with minimal turbulence.
It is generally known that the sludge of maritime waterways may be contaminated with toxic chemicals and heavy metals from accidental or illegal discharges or from seepage from industrial sites, such as, for example, pollution by toxic substances that are often present on the hull of a ship to repel the growth of marine organisms.
These harmful substances remain present in the sludge of port areas and maritime waterways. These pollutions around port areas have a detrimental effect on the local indigenous marine organisms.
However, a problem is that current dredging techniques to remove sludge from the bottom of a wetland are often relatively inefficient in the sense that they create a lot of turbulence, causing sludge churn as well as turbidity or muddiness in the water.
The water content in the sludge is increased by the churning during dredging. This is not interesting because to clean the pumped up sludge, the moisture content has to be completely or partially removed. An increased moisture content therefore makes the dredging process relatively more expensive and the cleaning of the pumped up sludge more time-consuming.
Another disadvantage of the turbulence caused is that the churned polluted sludge spreads out over the wetland by resuspension of the sludge and possibly mixes with unpolluted sludge, while in fact the dredging and removal of the sludge should remain in situ as much as possible.
In addition, the precipitation of the resuspended sludge completely disturbs or even completely destroys soil organisms.
One consequence of the risk that a lot of turbulence is created using traditional sludge removal techniques, is that such polluted water bodies are left untouched by the authorities to avoid the risk of further dispersal through churn and inefficient removal.
This implies that polluted port areas are not deepened or expanded any further, which means that these areas with potentially high economic value remain unused.
In BE 1.018.005 and BE 1.021.095 of the same inventor, techniques are already known for in situ dredging, using a diving bell which is pushed into the sludge to be removed and from which the enclosed sludge is pumped away.
The purpose of the present invention is to further improve these known techniques using a diving bell.
To this end, the present invention relates to a device for the underwater in situ removal of sludge and/or sand from the bottom of a wetland, the device containing:
This movable outlet of the compressed gas will allow the air above the sludge or sand to escape freely when the diving bell is driven into the sludge or sand, so that the diving bell can be filled with sludge or sand as much as possible without the water being driven out.
The outlet will always be above the sludge or sand to be removed and the float, together with the movable outlet and the supply of the compressed gas, ensure that the water level and the pressure above the water in the bell are self-regulating.
Indeed, the air in the diving bell will be able to escape through the outlet, and the water level will stabilise at the level of the upper edge of the outlet.
As the float and therefore also the outlet mounted on it follow the level of the sludge, the level of the water will also follow the level of the sludge or sand and therefore the level of the sludge or sand and the level of the water will decrease together as more sludge or sand is pumped away.
Because both levels drop at the same time, there is no flow of water through the sludge to the outside, so that the pollution cannot escape to the outside and, in other words, during dredging, the pollution is retained inside the diving bell.
Such automatic regulation of the level and pressure is very simple and very effective as has already been demonstrated in closed trials.
According to a practical embodiment, the aforementioned outlet is formed by the open end of a pipe which, through an opening at the top of the diving bell, releases into the environment and, for example, is guided above the water surface via a further pipe to prevent turbulence and turbidity caused by rising air bubbles or to be able to purify toxically charged air if necessary.
The float with the outlet on it is preferably suspended in the diving bell by means of a chain or the like, whereby the length of this chain is such that when the diving bell is taken out of the water, the float with its underside is approximately at the level of the lower edge of the diving bell and when the diving bell is driven into the sludge, the float immediately comes into contact with the rising sludge in the diving bell.
Preferably, the float is such that it floats on the sludge or sand, but still does not have sufficient buoyancy to, together with the weight of the pipe, float the compressed gas outlet on the water.
The float, for example, is formed by a sufficiently dimensioned sheet to support the weight of the pipe on the sheet on the sludge or sand.
According to a simple practical embodiment, the pipe is formed by a rigid metal tube which rests and is attached to the float with one end and, with the other end, releases into the outside environment of the diving bell via a flexible coupling at the top of the diving bell.
Preferably, the dredge pump is attached at a fixed location in the diving bell so that it is floated into the sludge together with the diving bell and the inlet of the dredge pump is situated at the level of the lower free edge of the diving bell.
To obtain the aforementioned balance in the diving bell, a compressor is used, the pressure of which is set to a maximum pressure higher than the pressure of a water column with a height equal to the difference in level between the water surface of the wetland and the lower free edge of the diving bell.
Optionally, the diving bell near the lower edge can be provided with one or more water jets that are fed by a jet pump that injects water into the sludge or sand, which can be useful when the sludge is a hard substance.
To drive the diving bell into the sludge, for example, a hydraulic crane or excavator with a hydraulic unit group that supplies the hydraulic power to drive the dredge pump and the optional jet pump, whereby the diving bell is suspended from the crane's arm, can be used.
For example, the hydraulic crane is installed on a work boat or pontoon, together with the aforementioned compressor.
The means to drive the diving bell into the sludge or the sand may include a vibration or pile-driving installation, which may be mounted on the crane, for example.
To allow the crane operator to see or know what he is doing, means can be provided to assess the depth of the diving bell in the layer of sludge or sand as well as means to assess the thickness of the sludge layer.
The invention also relates to a method for the underwater in situ dredging of sludge or sand.
With the intention of better showing the characteristics of the invention, some preferred embodiments according to the present invention are described hereinafter by way of an example, without any limiting nature, with reference to the accompanying drawings, wherein:
The device 1 according to the invention as shown in
The use of the device 1 according to the invention is simple and as follows.
Using the hydraulic crane 2 the diving bell 5 is pushed down and, together with the dredge pump 11, is driven into the sludge 14 with the blade at the lower edge 10 of the diving bell 5 in a horizontal position.
When the diving bell 5 reaches the level of the sludge 14 as in the initial situation of
When the diving bell 5 is driven into the sludge 14 at a depth A, as shown in
Because the space 6 in the diving bell 6 above the sludge 14 is always connected to the outside air, as the level of the sludge 14 rises in the space 6 of the diving bell 5, the air is driven out.
In the position of
When the dredge pump 11 is driven, the sludge 14 that is enclosed in the diving bell 5 is pumped away to the collector 17.
As the dredging progresses, the level of the sludge 14 in the diving bell 5 decreases and the float 27, and thus the level 29 of the water 30, follows the level of the sludge 14 in the diving bell.
The level 30 is controlled by pumping with the dredge pump 11 until all the sludge 14 in the diving bell 5 has been pumped out, as shown in
In other words, water is never driven out that could otherwise cause pollutions present in the sludge to be rinsed out.
In this way, only the sludge 14 that is caught in the diving bell 5 is dredged without disturbing the sludge 14 all around.
The level 29 of the water 30 above the level of the sludge therefore depends on the height of the upper edge 31 of the outlet 25 and can therefore be regulated by positioning it higher or lower in relation to the float 27.
Preferably, the float 27 is designed to float on the sludge 14, but yet does not have sufficient buoyancy in water to, together with the weight of the pipe 24b, float on the water, so that the float 27 can lower down on to the sludge 14.
To this end, the float 27 can be made as a simple sheet dimensioned in such a way that the pressure exerted by the sheet on the sludge by the weight of the tube 24b is less than the load-bearing capacity of the sludge.
Alternatively, the tube 24b can also be replaced by a flexible hose, the lower end of which is attached to the float 27 and whereby if necessary the float 27 is weighted to allow it to sink into the water on to the sludge.
The compressor 21 is set so that the maximum pressure is higher than the pressure of a water column with a height equal to the difference in level C between the water level 26 of the wetland and the blade at the lower free edge 10 of the diving bell 5.
After all the sludge 14 has been pumped out of the diving bell 5, the diving bell 5 can be driven deeper into the sludge 14 to be able to remove the deeper sludge 14 as well.
If necessary, an underlying sand layer 14′ with a higher density can also be removed up to a certain depth, in which case the diving bell 5 must be driven into the sand 14′ to this depth.
In this case or in the case of relatively compact sludge 14, the hydraulic crane can be equipped with a vibration or pile-driving installation to vibrate or pile-drive the diving bell into the sand or the sludge.
After dredging to the desired depth, the diving bell 5 can be pulled up again to be driven back into the sludge at another location to dredge there. In this way, consecutive dredging operations can efficiently clean up an entire area in a short period of time.
The crane 2 and the compressor 21 do not necessarily have to be mounted on a pontoon 3, but can also be installed on a quay, for example.
It is clear that instead of the hydraulic crane 2, also other means are conceivable for driving the diving bell 5 into the sludge.
The dredge pump 11 does not necessarily need a fixed position in the diving bell 5, but can, for example, be attached to a device that can move the dredge pump 11 in the diving bell 5.
Several dredge pumps 11 may also be provided.
In the example shown, the diving bell 5 is provided with means of transport 42 to move the dredge pump 11 horizontally and/or vertically within the diving bell 5 and with a vibration device 43 to vibrate the diving bell 5 in the sludge 14 and/or the sand 14′.
The present invention is by no means limited to the devices described by way of an example and shown in the figure, but, a device and a method for the removal of sludge according to the invention can be realised in all kinds of ways, without departing from the scope of the invention.
Number | Date | Country | Kind |
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2018/5630 | Sep 2018 | BE | national |
Filing Document | Filing Date | Country | Kind |
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PCT/IB2019/057693 | 9/12/2019 | WO | 00 |