CN107879469B - Partial nitrosation starting and controlling method - Google Patents
Partial nitrosation starting and controlling method Download PDFInfo
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Abstract
The invention discloses a partial nitrosation starting and controlling method, belongs to the field of sewage treatment, and solves the problems of difficult starting, unstable nitrite accumulation effect and the like in the conventional nitrosation process. The method comprises the steps of nitration start, intermittent aeration start, nitrite accumulation rate regulation, ammonia oxidation rate regulation, nitrosation stable operation control and the like, wherein the final ammonia nitrogen oxidation rate is stabilized at 55-60%, the nitrite accumulation rate is stabilized at least equal to 92%, and the ammonia nitrogen removal surface load is not less than 0.60gN/(m & ltn & gt)2D) meeting the nitrogen requirement of the subsequent anammox. The partial nitrosation effect of the invention is stable, the ammonia nitrogen oxidation load is high, the occupied area is saved, the operation is simple, and the operation is reliable; compared with the traditional process, the method can realize the selection and elimination of microorganisms and prevent the instability of long-term operation; high oxygen utilization rate and low energy consumption for aeration and fluidization.
Description
Technical Field
The invention belongs to the field of sewage treatment, and particularly relates to a partial nitrosation starting and controlling method.
Background
ANAMMOX (ANAMMOX) is NO2 -N is an electron acceptor, CO2As inorganic carbon source, under anaerobic condition, NH4 +Oxidation of-N to N2The biological process of (1). Compared with the traditional nitrification-denitrification process, the ANAMMOX process has the advantages of saving 50% of aeration amount, saving 100% of organic carbon source and the like, so that the ANAMMOX process has attracted the wide interest of a plurality of researchers once being found.
Because ammonia nitrogen and nitrite nitrogen in a ratio of 1:1.31 are required as substrates in the anaerobic ammonia oxidation process, a pretreatment process is required to partially oxidize the ammonia nitrogen into nitrite nitrogen without generating nitrate nitrogen, namely, a partial nitrosation process, also called a nitrosation process and a short-cut nitrification process. Part of nitrosation process directly determines whether the anaerobic ammonia oxidation process can be successfully realized.
The control key points of the partial nitrosation process are two, firstly, the nitration process is controlled in NO2 -Stage, blocking of NO2 -Further oxidized to NO3 -Namely enriching AOB (ammonia oxidizing bacteria) and inhibiting NOB (nitrite oxidizing bacteria); secondly, ensure the ammonia nitrogen and nitrite in the effluentThe ratio of nitrate nitrogen is around the theoretical coefficient of anammox of 1.31, generally 1: 1.2-1.35.
Currently, the main control means in the research include pH, T, FA, DO, etc. But for normal-temperature low-substrate sewage, DO regulation and control means are more in line with the actual conditions of engineering; for high-temperature high-substrate sewage, the high-temperature high-substrate sewage is regulated and controlled only by T, FA, and the system is easy to gradually destabilize after long-term operation and is converted to the whole nitrification direction. Therefore, part of nitrosation process and DO regulation are in the core position, and a large amount of related researches are carried out at home and abroad.
In DO regulation, the traditional method is carried out by adopting an oxygen limiting mode, and NOB is inhibited by utilizing the difference of AOB and NOB oxygen saturation constants. Studies have shown that under single DO or FA conditions, NOB is inhibited for a short period of time, but after long-term operation, NOB can gradually adapt to the corresponding conditions, while providing a varying gradient of DO is an effective means to prevent adaptive enrichment of NOB. The specific gradient DO regulation and control modes are researched more, have advantages and have certain problems.
The start and operation of the nitrosation process are realized by adopting an intermittent aeration control mode of 2h aeration/1 h aeration stop for the formation of the nitrite and the like (formation of the nitrite, SBR fast realizes short-range nitrification and influencing factors, environmental engineering report, 2015,9(5):2272, 2276); the intermittent aeration mode adopted by Sudonxia and the like is that the aeration/aeration stop time is 30min/10min (Sudonxia. SBR short-range nitration experimental research of different aeration modes, university news of China and south (Nature edition), 2014,45(6):2120 and 2129); controlling intermittent aeration in such a way that the aeration-stop time ratio is 1:1, and the aeration time is 5min, 15min, 30min and 45min respectively, and researching the aeration frequency on NO2 -The influence of the-N accumulation effect determines that when the aeration frequency is controlled to be 15 min/15 min, the aeration stop time point can be properly controlled to be just finished in the nitrosation reaction and not started in the nitrification reaction, so that the nitrosation becomes the dominant reaction, and further the NO is realized to the maximum extent2 -Accumulation of-N (Liyafeng. realization of SBR nitrosation under different aeration modes and NO2 -Environmental engineering journal, 2014,8 (11): 4561-4567); study of different aeration frequencies versus short distance under the condition of aeration-stop time ratio of 1:1Influence of nitrification (Liyafeng. influence factor of short-cut nitrification by intermittent aeration Shenyang university of buildings (Nature science edition), 2013,29(6): 1104-. Sudonxia and the like research different aeration-stop time ratios (3:1, 3:2 and 3:3) of 30min/10min, 30min/20min and 30min/30min respectively on nitrite nitrogen accumulation and nitrosation stability (Sudonxia. the influence of the aeration-stop time ratio on the short-range nitrification of the intermittent aeration SBR. Chinese environmental science 2014,34 (5): 1152-1158); on the basis of SBR process and pH value of inlet water of 8.2-8.5, various control means are respectively adopted to realize short-cut nitrification, including aeration for 5 min-aeration for 5min and aeration stop for 5min, and aeration quantity is not controlled; aeration is stopped for 5min to 15min without controlling aeration quantity; aerating for 15 min-stopping aeration for 15min without controlling aeration amount; aeration for 5 min-aeration for 5min, and stopping aeration for 5min, and a mode of limiting dissolved oxygen (zhanghui, preliminary experimental research of a new path of intermittent aeration short-cut nitrification control, Xinjiang environmental protection 2005,27(4): 28-32); enriching nitrosobacteria (Li Su Peak. realization of short-cut nitrification under intermittent aeration condition and influence factor research. environmental engineering report 2011, 5(7): 1518-.
The above studies all adopt an activated sludge process, and in an intermittent flow system, an intermittent aeration means is implemented to obtain DO gradient control to realize nitrosation. In the intermittent flow process, the intermittent aeration only influences the aeration time, and the requirement of the ammonia oxidation rate can be met by prolonging the HRT. Meanwhile, the aeration time and the aeration stopping time are fixed in the research, and the analysis and comparison are carried out, so that the obtained results are obtained under specific conditions and specific water quality, the universality is avoided, and the regulation and control methods and the basis of the aeration time and the aeration stopping time are not given; and the proportion of the effluent ammonia nitrogen and the nitrite nitrogen cannot be controlled, and the effluent cannot be directly used in the anaerobic ammonia oxidation process and needs to be prepared. However, in the engineering, it is not described how to implement intermittent aeration control in continuous flow while ensuring ammonia oxidation rate (55-60%) and nitrite accumulation rate (> 90%). In the continuous flow, because water still enters when the aeration is stopped, the intermittent aeration mode needs to be different from the intermittent flow in a time control mode, not only can provide the gradient DO, but also has small influence on the water outlet effect, and needs to ensure that the treatment capacity is not obviously reduced.
Although studies have been made to control DO levels in different aeration zones in a continuous flow by an activated sludge method, respectively, to achieve gradient DO control, inhibit NOB, and achieve nitrosation (mawarong. a/O biological denitrification process for domestic sewage treatment, study of short-cut nitrification and denitrification [ J ]. environmental science bulletin, 2006,26(5): 703-, zhangzhao, study on start of shortcut nitrification of low ammonia nitrogen sewage at normal temperature, China water supply and drainage, 2012 and 28, (9): 35-39). However, in actual operation, the sludge concentration in the system is gradually reduced, and finally the system is broken down, so that the long-term stable operation is difficult. The main reason for analysis is that in the nitrosation system, the functional flora AOB is autotrophic bacteria, has small specific growth rate, slow growth and poor settling property, is easy to run off along with effluent, and is more suitable for the autotrophic system by adopting a biomembrane method.
The traditional biomembrane method needs back washing, and the sludge age of the biomembrane is difficult to control, so nitrosation is not easy to realize. In the MBBR process, the filler is in a suspended state and fluidized along with aeration, so that the MBBR process has the characteristics of an activated sludge method and a biofilm method, and can obtain a better nitrosation effect.
MBBR (Moving Bed Biofilm Reactor) increases biomass and biological species in a Reactor by adding a certain amount of suspension carriers into the Reactor, thereby improving the treatment efficiency of the Reactor, the density of the suspension filler is close to water, the density of the suspension filler is close to that of water before and after Biofilm formation, so that the suspension filler can be suspended in water.
The MBBR process has the following main characteristics:
1) the specific surface area is large. SuspensionThe floating filler is provided with a plurality of grooves and a net rack by adopting an internal hollow structural mode, so that the specific surface area of the filler is greatly increased. The specific surface area of the suspended filler is 450m2/m3In the above, the increase of the specific surface area greatly increases the number and concentration of the biological films attached to the surface of the filler;
2) the reaction form is good. The suspended stuffing is in fluidized state inside the reactor, and has reaction form similar to that of completely mixed reactor, contact with gas and water, raised mass transfer effect between the biomembrane on the stuffing and the nutritive matter in water, no water head loss in the suspended stuffing layer and homogeneous water and gas distribution. In addition, under the fluidization state, the aged biological membrane can automatically fall off through hydraulic flushing, and the updating of the biological membrane is promoted;
3) the oxygen utilization rate is high. The utilization rate of oxygen can be greatly improved by the cutting action of the packing layer and the continuous contact of the packing with water flow and air flow. The oxygenation performance of the perforation aeration system is compared when different fillers are added, and the oxygen transfer coefficient of the aeration system is increased to 9.7 percent from 4.4 percent when no filler is added under the condition of the adding rate of the filler;
4) the biological selectivity is good. Due to the structure of the filler, the micro-environment of different gradient dissolved oxygen of microorganisms is provided, and a good short-range nitrification effect can be maintained when the dissolved oxygen of the solution is high, so that the reaction rate is improved, the treatment load is increased, and the occupied area is reduced; fluidization promotes the updating of the biological membrane, controls the sludge age of the biological membrane and prevents the enrichment of nitrite oxidizing bacteria;
5) in addition, the suspension filler can be directly added into the water tank without any support and installation engineering, and the addition and the updating are also very convenient. In actual operation, the suspended filler is not easy to agglomerate and block in the fluidization process, a back washing facility is not needed, and the management and maintenance work is simpler.
In the research of the MBBR method, Deng \23252ischaracterized in that a self-made continuous ideal mixing CSTR (continuous ideal mixing Tankreactor) is adopted to culture enriched nitrite bacteria, through manual diversion, 50% of wastewater is subjected to complete nitrosation conversion, in addition, 50% of wastewater is directly drained and combined with effluent of a previous process to perform anaerobic ammonia oxidation reaction, and DO of the reactor is controlled to be 1.5-2.0mg/L (research of a complete nitrosation autotrophic biomembrane in a moving bed biomembrane reactor, Master university, Hunan university, 2007); duyue et al have conducted deep shortcut nitrification research on landfill leachate subjected to anaerobic decarburization treatment by using aerobic MBBR, and the result shows that the DO concentration is 2mg/L as the best process condition (Duyue. moving bed biofilm reactor for landfill leachate shortcut nitrification research. environmental science, 2007, 28(5): 1039-; the study of the SHARON process of the municipal landfill leachate is carried out by MBBR in the aspects of meeting light and salary, etc., the filling ratio of the filler in the reactor is 60 percent, and the reactor can stably realize partial nitrosation (meeting light and salary. moving bed biofilm reactor SHARON process semi-nitrosation characteristic. chemical industry, 2008, 59 (1): 201-. Although the research shows that nitrosation is realized in the continuous flow MBBR process, the research is mostly carried out under favorable conditions, such as high T, pH, FA and the like, nitrosation is easily realized, DO still belongs to single control, and the long-term operation faces the risk of losing stability.
In the MBBR system, although the operation mode is similar to that of an activated sludge process, the essential difference is that in the activated sludge process, microorganisms are completely mixed, go from the beginning end to the end of a reactor, then flow back, and run to each area, and gradient DO control can be realized by setting different lattices which are respectively aerobic sections or anoxic sections; in the MBBR, microorganisms are fixed to the packing, and are fluidized only in the fixed zone, and cannot travel to each zone, and the gradient DO control means of the activated sludge method is not effective in the MBBR. Sheath 28952as a filler with a filling rate of about 50%, the reactor runs continuously all day long, more studies on the nitrosation performance of the system are carried out, including adopting a high-aeration-quantity intermittent running mode and a low-aeration-quantity intermittent running mode, and respectively setting DO <0.5mg/L, 0.5-1.0mg/L, 1.0-2.0mg/L and >2.0mg/L, studying the optimal nitrosation DO concentration, and achieving a nitrite nitrogen accumulation rate of 75.94%, thereby basically realizing short-distance nitrodenitrification (Yan cover. study of short-distance nitrodenitrification denitrification by moving bed biomembrane university, Hunan university, 2011); similar studies have been performed in Korea (Korea. MBBR Process short cut nitrification influencing factor study. Water supply and drainage 2015, 41 (1): 124- & 128). However, the nitrite accumulation rate in the research is low, and the requirement of nitrosation cannot be met; the intermittent aeration mode is DO level observation and non-control means, the whole period is as long as 30d, and a regulation and control method is also provided; the duration of the study is short, and the stability of the system cannot be shown.
In the prior patent, a short-cut nitrification process starting and operating method based on MBBR adopts a continuous aeration method, belongs to MBBR continuous flow operation, and simultaneously gives out DO controlled in the range of 1.2-3.5mg/L, but still belongs to a single DO system, and is likely to face the risk of instability in long-term operation; meanwhile, the proportion of the effluent ammonia nitrogen and the nitrite nitrogen cannot be controlled, and the effluent cannot be directly used in the anaerobic ammonia oxidation process and needs to be prepared. In the pretreatment method of the anaerobic ammonia oxidation process based on the MBBR, although the control method gives how to regulate the proportion of the effluent ammonia nitrogen and the nitrite nitrogen, the control method still belongs to a single DO system, and if DO gradient change cannot be formed in the system, the system is difficult to stably operate for a long time. The AOB has strong adaptability to DO fluctuation, while the NOB has poor adaptability to DO fluctuation, and particularly, the DO fluctuation is more effective for screening the AOB and the NOB at low temperature and low ammonia nitrogen.
In conclusion, in the existing research on nitrosation, for an intermittent flow activated sludge system, the nitrosation can be effectively controlled by adopting intermittent aeration; in a continuous flow activated sludge system, the supply of gradient DO can be realized by setting alternate aerobic and anoxic sections, NOB is inhibited, but the sludge concentration is gradually reduced after long-term operation, and the system is broken down; in the biomembrane method, the MBBR adopts a constant DO mode, and the long-term operation of the system faces instability risk; meanwhile, nitrosation in research does not provide influent water with a suitable nitrogen proportion for anaerobic ammonia oxidation, and effluent water is difficult to use for anaerobic ammonia oxidation influent water. Formally, due to these technical problems and technical deficiencies, improvements and optimizations are needed.
The nitrosation effect is generally evaluated by the nitrite accumulation rate. The nitrite accumulation rate is the ratio of the nitrite nitrogen generation amount to the sum of the nitrite nitrogen and nitrate nitrogen generation amounts in the reaction process, namely (effluent nitrite nitrogen-influent nitrite nitrogen)/(effluent nitrite nitrogen-influent nitrite nitrogen + effluent nitrate nitrogen-influent nitrate nitrogen), and generally, when the nitrite accumulation rate is greater than 90%, the nitrosation effect is good.
The ammoxidation rate refers to the ratio of ammonia nitrogen oxidized in the reaction to the ammonia nitrogen in the inlet water, namely (inlet ammonia nitrogen-outlet ammonia nitrogen)/inlet ammonia nitrogen, and the optimal ammoxidation rate is 55-60% for anaerobic ammoxidation.
The processing capacity of the biochemical system is measured by adopting load, and the load is divided into volume load, sludge load and surface load according to different types of reactors. The volume load takes the processing capacity of a unit volume reactor as an evaluation standard; the sludge load takes the sludge treatment capacity per unit mass as an evaluation standard; the surface load is evaluated by the treatment capacity per unit area of the biofilm. Because the MBBR technology is a biological membrane system, the surface load measurement is more scientific and accurate.
The ammonia nitrogen inlet surface load, namely the unit biological membrane area, the mass of the ammonia nitrogen entering the system born every day, and the unit is gN/(m)2D), equal to the daily ammonia nitrogen mass entering the system/total area of the biological membrane in the system.
The ammonia nitrogen removes the surface load, namely the unit biomembrane area, the quality of ammonia nitrogen removed every day, the unit is gN/(m)2D) equal to the mass of ammonia nitrogen removed per day of the system/total area of the biofilm in the system; the ratio of the ammonia nitrogen removal surface load to the ammonia nitrogen inflow surface load is the ammonia oxidation rate; and adjusting the ammonia nitrogen removal surface load, including adjusting the water inflow or the ammonia nitrogen concentration of the inflow.
To prevent the contingent data from affecting the system decision, the nitrite accumulation rate was determined as a continuous 3-day average increase over 5 days. For example, if the 1-3d nitrite accumulation rates are 9%, 11%, and 10%, respectively, the 3 rd day average of the 3 rd nitrite accumulation rate is 10%; the nitrite accumulation rates of 5-7d are respectively 18%, 20% and 22%, and the 3-day average value of the nitrite accumulation rate of 7d is 20%; the accumulation rate of nitrite increased by 10% in 5 days from 3d to 7 d.
Specific surface area of suspended filler, i.e. the surface area of the naturally piled suspended carrier contained in a unit volume, expressed in m2/m3。
The suspension packing porosity is the ratio of the volume of the pores between the suspension carriers to the volume of the container by filling the container with the suspension carriers per unit volume (natural packing).
Disclosure of Invention
In order to solve the problems that the continuous flow operation is difficult in the nitrosation process, the effluent nitrogen proportion is unstable, the long-term operation is easy to convert into the whole nitrification process, the sludge concentration of the system is difficult to maintain and the like in the prior art, the invention provides a partial nitrosation starting and controlling method, and the method has the advantages of continuous operation, stable treatment effect, capability of ensuring the long-term operation stability, accurate control of the effluent nitrogen proportion, convenience in management and maintenance and the like.
A partial nitrosation starting and controlling method is characterized in that inlet water continuously passes through a biological filler filling reactor, and partial nitrosation is realized by adopting an intermittent aeration mode, and the method specifically comprises the following steps:
1) starting nitration, filling biological filler with filling rate of 20-70% in the reactor, starting water inlet continuous flow operation after preliminary film hanging of stuffy aeration, and controlling DO>3mg/L, maintaining the ammoxidation rate>70 percent, gradually increasing the surface load of ammonia nitrogen inflow until the surface load of ammonia nitrogen removal is more than or equal to 0.80 gN/(m)2·d)；
2) Starting intermittent aeration, operating in an intermittent aeration mode, wherein the initial aeration time is 15-40min, the initial stirring time is 15-40min, and controlling the ammoxidation rate>70 percent, gradually increasing the surface load of ammonia nitrogen inflow until the surface load of ammonia nitrogen removal is more than or equal to 0.70 gN/(m)2D) fixing the HRT run;
3) regulating and controlling the nitrite accumulation rate, operating in an intermittent aeration mode, regulating the stirring time, and operating in the mode if the nitrite accumulation rate rises by more than or equal to 10 percent within 5 days of continuous 3-day average value; if the nitrite accumulation rate is increased within 5 days after 3 continuous days<10 percent, prolonging the stirring time by 15 to 20 percent each time; the adjustment interval is not less than 5 d; until the ammonia nitrogen removal surface load is more than or equal to 0.60 gN/(m)2D), the nitrite accumulation rate is more than or equal to 92 percent;
4) regulating and controlling ammoxidation rate, operating according to an intermittent aeration mode and regulating DO, when ammoxidation rate>60 percent, and reduces DO by 0.1-0.2mg/L each time or reduces aeration time by 10-15 percent each time; when the ammonia oxidation rate is high<Increasing DO by 0.1-0.2mg/L each time or prolonging aeration time by 10-15% each time; the adjustment interval is not less than 5 d; until the ammonia nitrogen removal surface load is more than or equal to 0.60 gN/(m)2D), the ammoxidation rate is 55-60%;
5) controlling the stable operation of nitrosation, adjusting according to the step 3) and the step 4), and controlling the surface load of ammonia nitrogen removal to be more than or equal to 0.60 gN/(m)2D), the nitrite accumulation rate is more than or equal to 92 percent, and the ammonia oxidation rate is 55-60 percent.
As well known by people in the industry, the stuffy aeration adopts intermittent flow operation, 3-4g/L of activated sludge in an aeration tank of a sewage plant can be inoculated into a reactor, the operation is performed according to the cycle of water inlet, aeration, sedimentation and drainage, the speed of film formation of a filler is increased, the sludge in the reactor is emptied after a thin layer of biological film appears on the surface of the filler, and continuous flow operation is started; or directly inoculate the biofilm-coated biological filler to accelerate the starting speed.
Preferably, the BOD: TN is less than 0.2, and SS is less than 50 mg/L.
As is well known to those skilled in the art, the influent water requirements are typically met by decarbonizing the wastewater by pretreatment, including biological or physical-chemical treatment.
Preferably, the biological filler has a specific surface area of 450-1600m2/m3The proportion of the filler before film formation is 0.93-0.99, and the porosity is more than or equal to 90%.
Preferably, the concentration of the suspended sludge in the reactor is less than or equal to 1.0g/L, water continuously enters and exits the reactor, and the temperature of the water in the reactor is higher than 12 ℃.
As is well known in the art, the reactor is not provided with sludge backflow, i.e., activated sludge retention is not performed, microorganisms mainly take an attached state (suspended filler biofilm) as a main body, but a dropped biofilm still exists in the reactor, and the suspended state concentration of the microorganisms is controlled by sludge discharge.
Preferably, the intermittent aeration mode alternately operates according to an aeration period, an aeration stop and a stirring period.
Preferably, the intermittent aeration mode has an aeration time not more than 1/5 of HRT, and the ratio of the aeration time to the aeration stopping and stirring time is 0.5-1.5.
Preferably, in the intermittent aeration mode and the aeration stage, DO is 1.1-2.5mg/L, and the DO value is 1.0-1.5 times of the surface load of ammonia nitrogen inlet water; the aeration gas-water ratio is more than or equal to 5.
As is well known by people in the industry, DO in the system is continuously changed according to the reaction process, and the DO in the aeration period is the average value of the aeration operation period 3min after the aeration is started; the aeration gas-water ratio, namely the ratio of the gas quantity to the water quantity in the reactor, is used for ensuring the fluidization of the filler and the updating of the biological membrane and preventing NOB accumulation caused by overlong sludge age. When the aeration gas-water ratio reaches the lowest limit of 5, the DO can be further reduced by changing the mode of the aeration device under the condition of not reducing the gas-water ratio.
The invention has the following beneficial technical effects:
1) the nitrosation process can realize the stable accumulation of nitrite nitrogen, and particularly, aiming at the conditions of low temperature and low ammonia nitrogen, the nitrite accumulation rate is always stable and is more than 92 percent after the nitrosation process is successfully started;
2) the nitrosation process has high treatment load, and the ammonia nitrogen removal surface load exceeds 0.6 gN/(m)2D) ammonia nitrogen removal volumetric load exceeding 0.17 kgN/(m)3D), much higher than the activated sludge process;
3) compared with an activated sludge process, the nitrosation process can realize long-term stable operation, the operation time exceeds 200d, and high-load and high-efficiency operation can be still maintained without attenuation;
4) compared with a fixed bed process, the nitrosation process has the advantages that the problems of red worm breeding, non-uniform water distribution, easy dead zone formation and the like are solved; compared with a fluidized bed process, the oxygen utilization rate is high, and the energy consumption of aeration fluidization is low; the device has the function of selecting the sludge age, realizes the alternate operation of aerobic and anoxic in a single functional zone in an intermittent aeration mode, and does not influence the effluent quality;
5) the nitrosation process has the advantages of adjustable volume load and the like, and the volume load is increased by 30-200% through the supplement of the suspended filler;
6) the nitrosation process of the invention can be operated in a new start-up mode and can also be carried out based on a started nitration system.
Drawings
The invention will be further described in detail and fully with reference to the accompanying drawings, in which:
FIG. 1 is a graph of nitrogen concentration and HRT of inlet and outlet water in a nitrosation process;
FIG. 2 is a graph showing ammonia oxidation rate, nitrite accumulation rate and load in the nitrosation process.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention clearer and clearer, the present invention will be further described in detail with reference to specific embodiments.
Under the condition of continuous flow, the suspended filler is used as a microorganism attachment carrier, and the microorganism is in a fixed state, which is different from the activated sludge method, and is more beneficial to the retention of AOB (ammonia oxidizing bacteria); meanwhile, different from a fixed bed biofilm reactor, the carrier is fluidized, the biofilm is updated in the fluidization process, and the NOB (nitrite oxidizing bacteria) is prevented from being accumulated due to overlong sludge age through gas-water ratio control; meanwhile, a more favorable condition is created for AOB enrichment and NOB elimination through an intermittent aeration mode. The low temperature and low ammonia nitrogen condition is more unfavorable for AOB enrichment and NOB elimination. The present invention, as shown in fig. 1 to 2, includes the following steps.
Example 1:
the volume of the reactor tank is 10m3Using a specific surface area of 700m2/m3Suspension carrier, suspension carrier specific gravity before film formation is 0.965, void ratio>95 percent; the reactor is not provided with sludge reflux, and the suspended sludge concentration in the reactor is always in the continuous flow running process<0.5 g/L; the inlet water is sewage obtained by decarbonizing domestic sewage, BOD of the inlet water is 10 +/-3 mg/L, TN is 55 +/-6 mg/L, ammonia nitrogen is 50 +/-5 mg/L, and BOD: TN<0.2, water inlet SS<20mg/L and the water temperature is 15 +/-3 ℃;
1) starting nitration, filling suspension carrier 4m3The filling rate is 40 percent, DO is controlled to be 4-5mg/L, the sewage plant is inoculated with 4g/L of activated sludge for aeration, each period runs for 10 hours, and the sludge is discharged after precipitationDischarging supernatant, operating for 10 periods, emptying sludge in the reactor, continuously feeding water and aerating, controlling initial HRT (high temperature) to be 10h, controlling DO to be 4-5mg/L to 15d, controlling ammonia oxidation rate to be 74%, and removing ammonia nitrogen with surface load of 0.322gN/(m n) with ammonia nitrogen removal2D); gradually reducing HRT, controlling DO at 4-5mg/L, and when the time is up to 30d, the HRT is 4h, and the ammonia nitrogen removal surface load is 0.893 gN/(m)2·d)；
2) Starting intermittent aeration, starting the intermittent aeration operation, wherein HRT is 4h, and the surface load of the inlet ammonia nitrogen is 1.07 +/-0.12 gN/(m)2D), controlling DO at 1.5 +/-0.1 mg/L during aeration for 30 min; then stopping aeration and stirring for 30 min; then, the aeration, the stop of the aeration and the stirring are alternately operated according to the above steps, and the surface load of the ammonia nitrogen removal is 0.536 gN/(m)2D); when the ammonia nitrogen removal surface load reaches 40 days, the ammonia nitrogen removal surface load is 0.713 gN/(m)2D), at this time, the nitrite accumulation rate reaches 47.2%, and the ammonia oxidation rate reaches 60%;
3) regulating and controlling the nitrite accumulation rate, wherein DO is controlled to be 1.5 +/-0.1 mg/L during aeration, and the aeration time is 30 min; then stopping aeration and stirring for 30 min; then, the aeration is stopped and the stirring operation is carried out alternately according to the aeration; when the time reaches 48 days, the nitrite accumulation rate reaches 76.7 percent, and is not increased any more; the stirring time is prolonged to 35min, the aeration time is unchanged, the nitrite accumulation rate is 92% when the stirring time reaches 58d, and the ammonia nitrogen removal surface load is 0.541 gN/(m)2D), at which point the ammonia oxidation rate is 52%;
4) regulating and controlling the ammoxidation rate, wherein DO is controlled to be 1.5 +/-0.1 mg/L during aeration, and the aeration time is 30 min; then stopping aeration and stirring for 35 min; then, the aeration is stopped and the stirring operation is carried out alternately according to the aeration; from 59 days, the DO is increased to 1.7 +/-0.1 mg/L to 62 days, the ammonia oxidation rate reaches 57 percent, the nitrite accumulation rate reaches 94.3 percent, and the ammonia nitrogen removal load reaches 0.603N/(m)2·d)；
5) Controlling the stable operation of nitrosation, controlling the accumulation rate of nitrite, operating in an intermittent aeration mode, adjusting the stirring time, and operating in the mode if the average value of the accumulation rate of nitrite rises more than or equal to 10% within 5d after continuous 3 days; if the nitrite accumulation rate is increased within 5 days after 3 continuous days<10 percent of stirring time is prolonged, and each time is prolonged15 to 20 percent; the adjustment interval is not less than 5 d; the surface load of ammonia nitrogen removal is more than or equal to 0.60 gN/(m)2D), the nitrite accumulation rate is more than or equal to 92 percent; for the regulation of the ammoxidation rate, the operation is carried out according to an intermittent aeration mode, DO is regulated, and when the ammoxidation rate is higher than the preset value>60 percent, and reduces DO by 0.1-0.2mg/L each time or reduces aeration time by 10-15 percent each time; when the ammonia oxidation rate is high<Increasing DO by 0.1-0.2mg/L each time or prolonging aeration time by 10-15% each time; the adjustment interval is not less than 5 d; the surface load of ammonia nitrogen removal is more than or equal to 0.60 gN/(m)2D), the ammoxidation rate is 55-60%; the reactor had been operating steadily for over 200 days.
Parts not described in the above modes can be realized by adopting or referring to the prior art.
The foregoing is only a preferred embodiment of the present invention, and it should be noted that, for those skilled in the art, various modifications and decorations can be made without departing from the technical principle of the present invention, and these modifications and decorations should also be regarded as the protection scope of the present invention.
Claims (7)
1. A partial nitrosation starting and controlling method is characterized in that inlet water continuously passes through a biological filler filling reactor, and partial nitrosation is realized by adopting an intermittent aeration mode, and the method specifically comprises the following steps:
1) starting nitration, filling biological filler with filling rate of 20-70% in the reactor, starting water inlet continuous flow operation after preliminary film hanging of stuffy aeration, and controlling DO>3mg/L, maintaining the ammoxidation rate>70 percent, gradually increasing the surface load of ammonia nitrogen inflow until the surface load of ammonia nitrogen removal is more than or equal to 0.80 gN/(m)2·d)；
2) Starting intermittent aeration, operating in an intermittent aeration mode, wherein the initial aeration time is 15-40min, the initial stirring time is 15-40min, and controlling the ammoxidation rate>70 percent, gradually increasing the surface load of ammonia nitrogen inflow until the surface load of ammonia nitrogen removal is more than or equal to 0.70 gN/(m)2D) fixing the HRT run;
3) regulating and controlling the nitrite accumulation rate, operating in an intermittent aeration mode, regulating the stirring time, and increasing the nitrite accumulation rate within 5 days if the average value of 3 continuous daysNot less than 10 percent, and operating according to the mode; if the nitrite accumulation rate is increased within 5 days after 3 continuous days<10 percent, prolonging the stirring time by 15 to 20 percent each time; the adjustment interval is not less than 5 d; until the ammonia nitrogen removal surface load is more than or equal to 0.60 gN/(m)2D), the nitrite accumulation rate is more than or equal to 92 percent;
4) regulating and controlling the ammoxidation rate, operating in an intermittent aeration mode, regulating DO, and regulating the ammoxidation rate>60 percent, and reduces DO by 0.1-0.2mg/L each time or reduces aeration time by 10-15 percent each time; when the ammonia oxidation rate is high<Increasing DO by 0.1-0.2mg/L each time or prolonging aeration time by 10-15% each time; the adjustment interval is not less than 5 d; until the ammonia nitrogen removal surface load is more than or equal to 0.60 gN/(m)2D), the ammoxidation rate is 55-60%;
5) controlling the stable operation of nitrosation, adjusting according to the step 3) and the step 4), and controlling the surface load of ammonia nitrogen removal to be more than or equal to 0.60 gN/(m)2D), the nitrite accumulation rate is more than or equal to 92 percent, and the ammonia oxidation rate is 55-60 percent.
2. A partial nitrosation initiation and control process according to claim 1, characterised in that: the BOD, TN and SS of the influent water are less than 0.2 and 50 mg/L.
3. A partial nitrosation initiation and control process according to claim 1, characterised in that: the specific surface area of the biological filler is 450-1600m2/m3The proportion of the filler before film formation is 0.93-0.99, and the porosity is more than or equal to 90%.
4. A partial nitrosation initiation and control process according to claim 1, characterised in that: the concentration of suspended sludge in the reactor is less than or equal to 1.0g/L, water is continuously fed into and discharged from the reactor, and the temperature of water in the reactor is higher than 12 ℃.
5. A partial nitrosation initiation and control process according to claim 1, characterised in that: the intermittent aeration mode alternately operates according to an aeration stage, a stop aeration and a stirring stage.
6. A partial nitrosation initiation and control process according to claim 1, characterised in that: the intermittent aeration mode has the aeration time not more than 1/5 of HRT and the ratio of the aeration time to the time of stopping aeration and stirring is 0.5-1.5.
7. A partial nitrosation initiation and control process according to claim 1, characterised in that: in the intermittent aeration mode and the aeration stage, DO is 1.1-2.5mg/L, and the DO value is 1.0-1.5 times of the surface load of ammonia nitrogen inlet water; the aeration gas-water ratio is more than or equal to 5.
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| CN110745941A (en) * | 2019-09-27 | 2020-02-04 | 中车环境科技有限公司 | Deep denitrification method for sewage |
| CN110921824B (en) * | 2019-12-09 | 2021-11-16 | 南京大学盐城环保技术与工程研究院 | Culture method for denitrification capacity of anaerobic ammonia oxidation sludge |
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