CN1608678A

CN1608678A - Deodorizing and bacteriostasis method for exhaust pipeline of bath room and kitchen

Info

Publication number: CN1608678A
Application number: CNA200310111926XA
Authority: CN
Inventors: 吴明哲
Original assignee: Individual
Current assignee: Individual
Priority date: 2003-10-24
Filing date: 2003-10-24
Publication date: 2005-04-27
Anticipated expiration: 2023-10-24
Also published as: CN100340301C

Abstract

The deodorizing and bacteriostasis method for exhaust pipeline of bath room and kitchen includes: setting soluble deodorizing and bacteriostasis decomposing ferment in the water outlet; accumulating water and dissolving the decomposing ferment in water; flushing the pipeline with the accumulated water while increasing air content; decomposing the waste water and flushing matter with the decomposing ferment; exhausting the waste water with the decomposing ferment and the flushing matter to some fixed point; and further bacteriostasis decomposing of the waste water and the flushing matter with the decomposing ferment. The said process can eliminating the blocking matter in the exhaust pipeline while deodorizing and bacteriostasis effectively.

Description

Bathe the deodorization bacteriostasis method of kitchen discharge pipe

Technical field

The present invention is a kind of deodorization bacteriostasis method of bathing the kitchen discharge pipe.

Background technology

The general family of water closet that uses all is to use anaerobic tank usually, that is to say that feces is to mix with a large amount of water to be poured anaerobic tank more afterwards, therefore the thing that enters in the anaerobic tank contains the addle of many impurity for one, after addle is discharged in the pond, because flow velocity reduces, most float is just because of at the bottom of gravity is sunken to the pond, and is lighter than water, as oils and fats etc., then float on the water surface in the pond.Usually the time of staying of sewage in the pond be all more than 12 hours, at this moment between in have the float of 60%-70% to be trapped within the pond approximately.Anaerobic tank just is precipitation in this tens hour time of staying to the main purification function of this sewage, having only insoluble float to be removed the back by anaerobic tank discharges, and be not water purification from the water that anaerobic tank flows out, wherein still contain the float that is not removed and be bordering on the dissolubility refuse of one of percentage hundred.Therefore the sewage of handling through anaerobic tank still is sewage; Except containing dissolved matter and the float that is not removed, also can be dissolved with the product behind the bacterial digestion Organic substance, as ammonia, hydrogen sulfide, methane, carbon dioxide etc., well-known, ammonia and hydrogen sulfide all are to have malodorous gas.

For anaerobic tank is reached for the purpose of the higher sewage treating efficiency, new-type anaerobic tank often has the equipment of an aeration ditch, use by the processing of aeration and to remove these gases and some dissolved organic matters, general aeration ditch be designed to rectangular concrete ditch, every about half chi, place one on stone in the ditch, the effect of stone is to cause turbulent flow, makes effusive water have enough areas to contact with air, and airborne oxygen will constantly dissolve in the water till saturated.Under the supply that enough oxygen and nutrition (flow out water in organise thing and inorganicization thing) are arranged, on the surface of stone and furrow bank, will grow one deck rapidly and comprise aerobic organism, the microorganism of algae and protozoacide etc.Organise thing and inorganicization thing of a part of dissolubility will be absorbed by these microorganisms and remove, gas then is not that dissipation gradually is in air, be oxidized into stable inorganic salts exactly, certainly the difference of the degree of the handling composition that flows out water with the design situation and the anaerobic tank of ditch and environment (as temperature) and different.

Be with, in aeration process, increase with contacting of air, to make that the sewage degree of anaerobic tank is desirable more, and the processing of the aeration of existing anaerobic tank all is to entrust to be handled by professional institution, and its most way all is to insert a body in anaerobic tank, uses and squeezes into extraneous air, air in the aeration ditch is increased, yet this kind way real storage has a little weak point, and main cause is to be summarized as follows:

1, specialty office needs to adopt special-purpose utensil be poured into air outside, makes the entire equipment cost very expensive, and anaerobic tank for a long time just cleaning once, the cost that it spent is not worth it really.

2, some anaerobic tank just just is arranged on the bottom of building, makes cesspool cleaner truck usually need in the inlet chamber of trombone slide road, yet usually is subject to the place size, and be difficult to construction processing.

3, in work progress, the stench of anaerobic tank is dissipation thereupon, if still can accept reluctantly outdoor, in case anaerobic tank is arranged on when indoor, then the foul smell that it shed will make us being too bad to be accepted.

4, suitable of the manpower often employed of specialty office and material resources make the required expense of whole process with relative raising more, and expense is very considerable.

5, this kind work progress needs the engineering staff to enter sewer to carry out cleaning work usually, yet, the engineering staff enters sewer and poisons because of biogas because of improper ventilation is very easy often, so hear of when an engineering is unexpected, the traditional method for cleaning of this kind for the engineering staff, danger very.

Summary of the invention

Order of the present invention provides a kind of deodorization bacteriostasis method of bathing the kitchen discharge pipe, and purport is to make sewage of every discharging can reach the effect of bacteriostasis, and deodorization.

For achieving the above object, solution of the present invention is: the deodorization bacteriostasis method of bathing the kitchen discharge pipe:

A, elder generation are provided with the progressively amylase prescription of dissolved bacteriostasis, and deodorization at the place, water side;

B, store the water yield in advance, and amylase partly is dissolved in this storage water yield;

C, make this water storage that contains amylase wash away discharge tube, in the process of washing away, increase the air content in the water;

D, amylase carry out antibacterial decomposition because of waste water and the down wash that air content increases its discharging;

E, amylase is disposed to fixed point together with waste water and down wash thereof;

F, amylase carry out antibacterial decomposition once more to waste water in this fixed point and down wash;

After adopting such scheme, can effectively decompose hoarding and blocking of organic substance in the discharge pipe, and the stink and the antibacterial of exempting in the discharge pipe multiply.

Description of drawings

Fig. 1 is a schematic flow sheet of the present invention;

Fig. 2 is the sketch map that the present invention applies to toilet;

Fig. 3 is the sketch map that the present invention applies to tank.

1 amylase, 2 toilets

21 water tanks, 22 outlets

3 anaerobic tank, 4 tanks

5 amylases, 6 faucet

The specific embodiment

As shown in Figure 1, the present invention is a kind of deodorization bacteriostasis method of bathing the kitchen discharge pipe, it mainly is the amylase that employing one includes natural hay bacterium (Bacillus Subtilis), make its bag of making similar tea bag shape with adhesive-bonded fabric bag packing (or also can make the agent shape, ingot shape or annex solution etc.), because this kind hay bacterium can produce multiple metabolite and ferment, can hinder multiple fungus, the growth of antibacterial, multiply with the stink and the antibacterial of exempting in the discharge pipe, can effectively decompose hoarding and blocking of organic substance in the discharge pipe, so have an effect that is showing for harmful bacterium of eliminating in the pipeline, and using method of the present invention is:

B, store the water yield in advance, and this amylase partly is dissolved in this storage water yield;

C, disengage this water storage that contains amylase and washed away discharge tube, in washing away discharging process, increase the air content in the water by flowing of current;

D, amylase carry out antibacterial resolution process because of the increase of air content to waste water and the down wash that it discharged;

F, amylase can carry out antibacterial decomposition once more to waste water in this fixed point and down wash.

So, the amylase 1 in discharge water each time can decompose antibacterial processing again at waste water and the down wash in the fixed point.

Be with, if when applying to cistern, as shown in Figure 2, be to make amylase 1 be arranged in toilet 2 water tanks 21, it is can be made as the tea bag shape and hang among the water tank 21, be stored in the water tank 21 after outlet 22 each intake institute's entrained airs and amylase partly 1 dissolvings by toilet 2 water tanks 21, in the bath discharging process, owing to making, flowing of current carry a large amount of air in the water, make amylase 1 again at waste water that it discharged with carried out bacteriostasis, and deodorization by down wash, when being disposed to anaerobic tank 3 gatherings, because flowing of current, make in the discharge water each time amylase 1 again again at the waste water in the anaerobic tank 3 with carried out bacteriostasis, and deodorization by down wash, increase the efficient of aeration, use progressively and give deodorization and antibacterial processing at the organic substances in the anaerobic tank 3.

Moreover, the present invention also can apply in the tank 4 of combing platform as shown in Figure 3, in present embodiment, amylase 5 among the present invention is to make to become ingot shape thing and (also can make and form liquid or powder, being convenient to velocity of sound dissolving disengages), when being dissolved in water storage in the tank 4 as placement, can utilize the natural flows impulse force of faucet 6 water outlets to increase air content in the water, make amylase 5 be able to carry out bacteriostasis, and deodorization at the water liquid in the tank 4 handles in advance, as in waste discharge to sewer the time, because flow makes amylase 5 soluble in water to carry out decomposition and deodorization at the harmful bacterium in the pipeline again and handles.

Be with, the present invention can carry out primary bacteriostasis, and deodorization to harmful bacterium in the pre-pondage in advance and handle, also can be behind waste discharge carry out secondary processing at harmful bacterium at fixed point place such as in anaerobic tank or the sewer again, so, can in primary drainage procedure, progressively carry out antibacterial processing at sewer or anaerobic tank, the stink of sewer or anaerobic tank can be obviously reduced, and hoarding of organic substance can be reduced.

In sum, the deodorization bacteriostasis method of bath provided by the present invention kitchen discharge pipe, its method can be dredged hoarding, blocking of organic substance in the discharge pipe, and effectively deodorization and antibacterial, it is good obviously commonly using with mode effects such as artificial dredging sewer or anaerobic tank in fact, really having conformed with the relevant important document of invention, files an application in the whence in accordance with the law.

Claims

1, a kind of deodorization bacteriostasis method of bathing the kitchen discharge pipe, its deodorization bacteriostasis method is as follows:

C, make this water storage that contains amylase wash away discharge tube, in the process of flowing of washing away, increase the air content in the water;

Amylase in d, the water carries out antibacterial decomposition because of waste water and the down wash that air content increases its discharging;

F, amylase carry out antibacterial decomposition once more to waste water in this fixed point and down wash.