DE20022735U1 - Waste water treatment device - Google Patents

Description

TERMEER STEINMEISTER & PARTNER GBR PATENTANWÄLTE - EUROPEAN PATENT ATTORNEYS

Dr. Nicolaus 1er Meer, Dipl.-Chem. Peter Urner, Dipl.-Phys. Gebhard Merkle, Dipl.-Ing. (FH) Mauerkircherstrasse 45 D-81679 MUNICH

Helmul Steinmeister, Dipl.-Ing. Manfred Wiebusch

Artur-Ladebeck-Strasse 51 D-33617 BIELEFELD

CONSTRUCTION P01/99/EP/G-2

St/ec

6.12.2001

Markus Baumann

Taubenweg 4 32602 Vlotho

DEVICE FOR TREATMENT OF WASTE WATER

Priority:
25.02.1999 Federal Republic of Germany 199 07 980.3

Markus Baumann BAUP01/99/EP/G-2 ' 6.12.2001

DEVICE FOR TREATMENT OF WASTE WATER

The invention relates to a device for treating waste water in small sewage treatment plants and small sewage treatment plants with a number of units including an aerator, a clear water extraction pump, a sludge pump, etc.

The term "small sewage treatment plant" will be used in the following to represent both of the previously mentioned sizes of sewage treatment plants.

Small sewage treatment plants usually have a primary clarifier, a buffer tank and a treatment tank in which the actual biological treatment takes place. The primary clarifier and buffer tank can form a unit. In such cases, we will therefore only refer to primary clarifiers in the following.

Initially, it was common practice to construct the primary clarifier and the treatment tank as spatially separated, separate containers. Naturally, such a solution is complex and requires a considerable amount of space. So-called three-chamber tanks are therefore also common, in which three separate chambers are constructed within a common container.

DIN 4261, Part 2 and ATV A 122 and M 210 (information sheets from the Wastewater Technology Association) describe small sewage treatment plants that are used for so-called fully biological treatment. These plants have multi-chamber pits as primary clarifiers, which are usually followed by another tank containing the actual biological treatment stage. A biological treatment stage is often integrated into the tank of the multi-chamber pit. For this purpose, a so-called fixed bed system is usually used, in which solid bodies are placed in the corresponding chamber, on which microorganisms settle, breaking down the dirt particles from the wastewater.

So there are numerous known solutions.

The invention is based on the object of creating a small sewage treatment plant which can be set up for effective sewage treatment operation using conventional single-chamber or multi-chamber, in particular three-chamber containers with relatively few units.

Markus Baumann BAUP01/99/EP/G-2 ' " 6.12.2001

This object is achieved in a device of the above type in that the units are at least partially arranged on a common holder which can be inserted into and removed from a treatment tank of the treatment plant from above.
5

By hanging the units from above and in particular by combining several units in a common holder, the operation of the system is made considerably easier in terms of maintenance and care. While in many modern small sewage treatment plants units such as aerators, pumps, etc. are used individually and sometimes lowered to the bottom of the respective container, the invention only requires the installation of a single holder. Naturally, combining several units does not rule out the possibility of additional individual units being used separately in individual cases.

The holder can be at least partially supplemented to form a closed housing, particularly if water flows can be directed in a sensible manner through individual wall surfaces of the housing. For example, a housing base below the clear water extraction pump can be useful, as this prevents rising floating sludge from reaching the extraction pump. On the other hand, the downward-facing outlet of a submersible aerator, which directs an air-water jet towards the bottom of the tank, through which oxygen enters the water during the aeration process, should be completely free.

In particular, in the case of clear tanks in the form of three-chamber tanks, which are usually designed as cylindrical chambers with partition walls, the individual units can be placed or suspended on the partition walls. This option can be used in particular if three-chamber tanks are to be converted to the procedure provided for in the invention. In principle, at least four units would be required in these cases, namely a clear water extraction pump, an excess sludge pump, hereinafter referred to simply as a sludge pump, a submersible aerator and another pump that transfers incoming wastewater from the primary clarifier to the treatment tank or secondary clarifier. However, such pumps are relatively expensive and also require maintenance and are prone to failure.

Markus Baumann BAU POl/99/«¥G-2* "··"· ··«·!2.2091·

According to the invention, the sludge pump is therefore also designed to transfer the fresh clarification water from the primary clarification tank to the treatment tank. This can be done by attaching an outlet pipe to the outlet of the sludge pump, which pipe leads from the side of the treatment tank over the dividing wall into the primary clarification tank. With this pipe, water can be transferred from the primary clarification tank to the treatment tank using the principle of communicating pipes, as will be explained in more detail later.

Further features and advantages of the invention emerge from the subclaims.

In the following, preferred embodiments of the invention are explained with reference to the accompanying drawings.
15

Fig. 1 is a vertical section through an embodiment of a clarification device according to the invention;

Fig. 2 is a corresponding section and illustrates the night

drove;

Fig. 3 is an enlarged view of the upper portion of Fig. 1;

Fig. 4 is a vertical section through a device according to the invention.

when used in conjunction with a conventional three-chamber container;

Fig. 5 is a vertical section similar to Fig. 4;

Fig. 6 is a horizontal section of Figs. 4 and 5;

Fig. 7 shows a system with a three-chamber container similar to Fig. 4, but in a different embodiment;

Fig. 8 is a vertical section similar to Fig. 7, but in a 90°

offset level;

Fig. 9 is a plan view of Fig. 7 and 8.

Markus Baumann BAUP01/99/BfVG-2i ··· ··«·12.20»1·* ··«

In Fig. 1, a vertical container is designated 10. The container is composed of a cylindrical base part 12, two rings 14, 16 which can be placed on this and a head piece 18 which can be placed on the ring 16 and which converges towards the top and has an opening 20 in the center. The opening 20 is normally closed with a lid. It is usually dimensioned so that a fitter can climb into the container and so that the required units can be lowered into the container and installed. The base part 12, the rings 14, 16 and the head piece 18 are usually made of concrete. However, there are also corresponding containers which are made in one piece from plastic. Such containers are widely known and as such are not the subject of the present illustration. The embodiment shown therefore relates to a single-basin system.

On the left side in Fig. 1 and 2 an inlet 22 enters and on the right side an outlet 24 exits. The inlet 22 consists of a horizontal inlet pipe 26 and a vertical dip pipe 28 connected to this, open at the top and bottom, which is immersed deep into the waste water and catches and dampens the movement of the incoming fresh waste water and allows it to sink slowly into the tank. The outlet 24 comprises a horizontal pipe 30 exiting from the tank and a vertical dip pipe 32 upstream of this, into which only water from the area below the liquid level can enter, so that floating sludge from the surface is prevented from escaping through the outlet 24.

The outlet 24 essentially has the function of an emergency overflow, since the water contained in the tank is normally pumped out in the form of clear water via a pump, as will be explained below.

Below the opening 20 there is a frame 38 suspended from chains 34, 36 at the edge of the opening 20, which frame can be cylindrical, rectangular or in principle of any shape. In the embodiment shown in Fig. 1 and 2, the frame is cylindrical with a lower section 40 that tapers downwards and an upper section 42 that tapers upwards (Fig. 3). In the center of the upper conical section 42 there is a cover 44. In this embodiment, the frame is partially closed off by walls to form a housing.

Markus Baumann BAU POI/99^*5-2· ··· *·«·12.20»1· ···

The base, designated 46, consists essentially of a flange-shaped edge strip 48 and a central opening 50. Above the opening 50, in the vertical central axis of the overall cylindrical housing 38, there is a submersible aerator 52, which takes in air via a hose 54 leading to the outside and presses a water-air mixture vertically downwards through the opening using a conveyor screw (not shown). In this way, not only is air introduced into the water, but the strong water-air flow also serves to prevent sludge from settling during the aeration phase, which is normally during the day. The submersible aerator therefore also takes on the function of an agitator.

A clear water extraction pump 56 is located in a lateral position within the frame. The extraction pump 56 is thus located above the peripheral edge strip 48 of the base 46, so that rising floating sludge cannot get into the extraction pump 56, as can be seen in Fig. 2.

The extraction pump 56 is connected via a line 58 to a sample container 60, which consists of an outer container 62 and a removable inner container 64. The inner container can receive clear water via the line 58 and a pipe 66 that is connected to the line at the top. The clear water flows from the inner container into the outer container 62 via an overflow 68 at the upper edge of the inner container 64 and then out via a line 70. In the embodiment shown, the line 70 is led through the open end of the immersion pipe 32 into the horizontally exiting pipe 30 of the outlet 24. The water flows via the line 70 into a polishing pond, a receiving water or the like.

The pipe 66, through which the clear water is pumped into the inner container 64 with the aid of the clear water pump 56, is bent in an inverted U-shape and comprises a downward-running leg 72 which ends at a distance from the bottom of the inner container 64. This ensures that the clear water falls into the inner container 64 from a certain height, thus preventing sludge from accumulating in the sample vessel. This ensures that the contents of the inner container of the sample vessel are always flushed through, so that at the end of the clear water extraction phase, largely clear water that is representative of the state of the water remains for taking a sample.

Markus Baumann BAU P01/99/BP/G-2 ''"""0.12.2Ot)T "*

The tube 66 also has an upwardly directed vertical extension 74 which prevents the inner container 64 from being drained when the extraction pump 56 is switched off. The extension 74 can also be designed as a handle with the aid of which the entire tube 66 and the inner container 64 can be removed through the upper opening 20 when a sample is to be taken. The tube 66 is firmly and tightly connected to the bottom of the inner container 64.

Instead of the solution described above, a jacket pipe closed at the upper end can also be placed on the pipe 66, which surrounds the pipe 66 and ends at a distance from the bottom of the inner container 64. To ensure that the inner container is not drained dry at the end of the clear water discharge, the jacket pipe can have ventilation openings in the upper area. The design of the sample container therefore allows for several variations. In any case, the function should be guaranteed that the clear water is first let down from a certain height onto the bottom of the inner container 64, so that the accumulation of sludge is avoided and a sample is always available that is representative of the condition of the clear water when it leaves the system.

The tube 66 extends downwards beyond the unmarked bottom of the inner container 64 and can be pushed with this extension 76 into a guide tube 78 which passes upwards through the bottom of the outer container 62 and forms the upper end of a transition piece 80. This transition piece 80 is fastened in the wall of the upper conical section 42 of the housing 38 and forms the transition between the line 58 inside the housing 38 and the upper guide tube 78 to which the outer container 62 of the sample container is fastened. This can be seen in detail in Fig. 1 and 2 and in particular in Fig. 3. By pushing the lower extension 76 of the tube 66 into the guide tube 78, the tube 66 and the inner container 64 reach a fixed position with respect to the housing 38, in which they are held releasably.

In Fig. 1 to 3, a float 82 is schematically indicated, which belongs to a float switch (not shown). In this way, the fill levels in the container can be monitored and, if necessary, controlled by actuating the extraction pump 56 or a waste water feed pump (not shown).

Markus Baumann B AU PO 1 /99/BP/G-2"

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As can be seen in particular in Fig. 1 and 3, there are windows 84 distributed around the circumference in the walls of the frame 38 at the transition between the lower conical section 40 and the upper conical section 42, which are essentially at the level of the water surface and thus at the level of the floating sludge. Therefore, when the submersible aerator 52 is running, surface water and thus floating sludge is drawn through the windows 84 into the housing 38 according to the arrows shown in Fig. 1 and 3 and is pressed together with the water-air jet through the submersible aerator down to the bottom of the container. In this way, the formation of excessive floating sludge can be effectively suppressed.

Fig. 1 essentially corresponds to the situation towards the end of the day's operation. As the arrows indicate, a water-air flow is still being directed towards the bottom of the tank with the aid of the submersible aerator 52, while on the other hand the upper filling level shown in Fig. 1 to 3 has essentially been reached. Towards the end of the day the submersible aerator 52 is switched off. This calms the movement within the wastewater so that solid particles can settle and a clear water zone is created in the upper area. The strong air inflow during the day's operation has resulted in aerobic clarification. When the resting phase is over, the upper clear water layer is pumped outwards by the extraction pump 56 down to the lower limit level corresponding to the lower filling level line in Fig. 3, which is essentially at the level of the extraction pump 56, via the sample tank 60 and the line 70. The system shall be dimensioned such that the quantity withdrawn between the two water levels shown in Fig. 3 corresponds to the wastewater inflow normally occurring during the day.

Fig. 4 to 6 show a conventional three-chamber container in two vertical and one horizontal sections. The container can be retrofitted with a device unit according to the invention. The container designated 90 corresponds in terms of its external outline and shape to the container 10 according to Fig. 1 to 3, but is divided inside by a vertical partition 92 into two equal halves, one of which is further divided by a further partition 94 into two chambers of approximately a quarter of the total size of the container. This creates a first chamber 96 with a circumferential angle of 180° and a second and third chamber 98,100 with a circumferential angle of approximately 90°.

Markus Baumann BAUP01/99/EP/G-> ···" ·&idigr;·0!12.20&bgr;&Rgr;

The first chamber 96 takes over the function of the container 10 according to Fig. 1 to 3. The two other chambers 98, 100 serve to collect excess sludge. In this case, a cuboid-shaped frame 102 is provided which, as in the first embodiment, has a submersible aerator 52 and a clear water extraction pump 56. As in the first embodiment, a float switch 82 is also provided. A line 104 is used to suck in air, a further line 106 to discharge the clear water. The arrangement and mounting of the sample container 60 on the housing corresponds to the first embodiment. Fig. 4 shows that the entire unit is suspended with a hook (not shown) on the partition wall 92 in such a way that the frame 102 is immersed in the waste water in the larger chamber 96. The upper and lower water levels which occur during normal operation are shown in Fig. 4 and 5. It can be seen that the water level sinks during the night phase to approximately the level of the clear water extraction pump and rises during the day, with appropriate inflow, to the upper line indicated in Fig. 4 and 5.

The function corresponds to that of the embodiment according to Fig. 1 to 3. The two smaller chambers 98 and 100 serve to receive sludge, which is led from the chamber 96 into the chambers 98 and 100 by means of a transfer system 108.

Next, with reference to Figs. 7 to 9, a further embodiment of the invention will be described which, like the embodiment according to Figs. 4 to 6, is suitable for equipping or retrofitting a three-chamber container.

A frame 110 hangs from the partition wall 92 which divides the container 90 into two equal parts. This frame can be hung from above on the partition wall 92 and carries all the essential components of the system. A sludge pump 112, a submersible aerator 114 and a clear water extraction pump 116 are located on the frame 110. The clear water extraction pump is connected via a line 118 to a sample container 120, which in turn is connected to the pipe 30 on the side of the outlet 24. The clear water is therefore pumped via the line 118 into the sample container 120 and from there exits through the outlet 24. A standpipe 122 enters from below through the bottom of the sample container 120. This standpipe 122 serves as an emergency overflow in the event that the waste water in the container should "rise" above the upper level of the standpipe.

Markus Baumann BAU P01/99/fiP/G-2 6.12.20&I

The submersible aerator has the already described function of emitting a downward air-water flow which essentially reaches the bottom of the container 90. The submersible aerator 114 takes in air supplied from the outside via a line 124.

The sludge pump 112 pumps sludge water via an inverted U-shaped line 126 back into one of the two smaller chambers, in the example shown chamber 98. It also serves to take fresh dirty water that has entered chamber 100 via the inlet 22 and from there into chamber 98 into the larger chamber 96. The two smaller chambers 98 and 100 are connected through the wall 94 by openings 128 that are only indicated.

Fresh waste water, which enters chamber 100 via inlet 22 and is distributed from there into the two smaller chambers 98 and 100, is initially held back here so that solid sludge particles can settle and collect on the bottom. Chambers 98 and 100 therefore serve as sludge storage and also as buffers for incoming water. Incoming waste water is collected in chambers 98 and 100, while a biological purification process takes place in the large chamber 96.

The plant works according to the activated sludge principle in the damming process. The pollutants from the wastewater are absorbed by floating microorganisms (activated sludge) and converted into biomass. This will be explained in more detail in the following part of the description.

The actual purification process takes place in the larger chamber 96. Here, aeration is carried out periodically with the help of the submersible aerator 114, which introduces the oxygen necessary for aerobic purification. Then a settling phase occurs for a further period of time, in which the water in the chamber 96 is kept at rest and sludge particles can sink. When the water has reached the higher level 130, clear water is pumped out at the end of the settling phase in the manner already described until the lower level 132 is reached. Then freshly added water from the chambers 98,100 is transferred to the treatment chamber 96. This is done by using the sludge pump 112 to give a short pumping stroke, which fills the line 126 completely with water. When the pump 112 is switched on again

Markus Baumann BAU P01/99/EP/G-2 ·"·· ·*·&bgr;.12.20&Mgr;

10 -

is switched off, the waste water from the chambers 98,100 is drawn into the treatment chamber 96 via the water-filled line 126 according to the principle of communicating pipes. This takes place without energy consumption. When essentially the same level is reached in all three chambers, a purification process with the two phases described begins again in the treatment chamber 26.

First, the submersible aerator 114 is switched on. Below the sludge pump 112 there is a bowl that is open at the bottom and not shown in detail. This bowl surrounds the lower intake opening but leaves the intake opening free. The aeration air from the submersible aerator 114 creates air bubbles in the water, some of which collect in the bowl described and from there enter the line 126. The incoming air interrupts the closed water filling of the line 126 so that the water contained in the line 126 flows out in both directions. The function as a communicating tube is therefore switched off for the clarification process that has already started in the chamber 96. Aeration continues in the treatment chamber 26 with the help of the submersible aerator. This phase, which takes six hours, for example, is then followed by a settling phase in which solid particles can settle. The sludge pump 112 also has the function of returning sludge-containing waste water from the chamber 96 to the chamber 98 from time to time.

The sludge that gradually settles in the two chambers 98,100 is removed at regular intervals and disposed of as sewage sludge, or reused if necessary. The times for returning the sludge to the chambers 98,100 depend on the amount of dirt that has entered the treatment chamber 96. The sludge pump pumps a constant amount of activated sludge into the chambers 98,100 in each cycle.
30

The entire system is controlled electronically and can be adapted to the respective requirements, in particular to the amount of wastewater generated. The operating time of the submersible aerator and the clear water pump as well as the operating time of the sludge pump can each be set separately.
35

Markus Baumann BAUP01/99/EP/G-2 ··· •••g.l2.2(Jtfl **'

Since the pumping process only lasts for a short time, the purified water is collected in a sample container 120 so that representative clear water is available to the sampler at all times. The sample container is located near the upper opening of the container and is therefore easily accessible. All units arranged on the frame 110 can be removed upwards through the opening of the container using this frame for inspection and maintenance purposes.

The device according to the invention is therefore particularly suitable for equipping conventional three-chamber containers, but not only for these. It can therefore also be used successfully in systems with several separate basins, for example.

Claims (7)

1. Device for treating waste water in small sewage treatment plants and small sewage treatment plants with a number of units including an aerator ( 114 ), a clear water extraction pump ( 116 ) and a sludge pump ( 112 ), characterized in that the units are at least partially arranged on a common holder ( 38 , 102 , 110 ) which can be inserted into and removed from a sewage treatment tank ( 10 , 90 ) from above. 2. Device according to claim 1, characterized in that the clarification tank ( 90 ) is a three-chamber tank and that the holder ( 102 , 110 ) and optionally further units are placed or suspended on one of the partition walls ( 92 , 94 ) of the three-chamber tank. 3. Device according to claim 1, characterized in that the clarification tank ( 10 ) is a single-basin tank with an upper opening ( 20 ) and that the holder ( 38 ) is suspended in the region of the edge of the opening by means of tension members ( 34 , 36 ), in particular chains. 4. Device according to claim 2, characterized in that a submersible aerator ( 114 ), a clear water extraction pump ( 116 ) and a sludge pump ( 112 ) are arranged on the holder ( 110 ). 5. Device according to claim 4, characterized in that the three-chamber container has at least one pre-clarification chamber ( 98 , 100 ) and at least one treatment chamber ( 96 ) and that the sludge pump ( 112 ) is arranged on the partition wall ( 92 ) between the two on the side of the treatment chamber ( 96 ) and is connected to the pre-clarification chamber ( 98 , 100 ) via an outlet line ( 126 ) across the partition wall. 6. Device according to claim 5, characterized in that the submersible aerator ( 114 ) is arranged adjacent to the sludge pump ( 112 ) and that a downwardly open collecting tray is provided on the underside of the sludge pump, which is connected at the top to the outlet line ( 126 ). 7. Device according to one of claims 4 to 6, characterized in that a line ( 118 ) runs from the clear water extraction pump ( 116 ) into a sample container ( 120 ), the overflow of which is connected to the pipe ( 30 ) of the drain.