APPARATUS AND METHOD FOR MEASURING NOx AND NITRIFICATION/DENITRIFICATION RATES IN BIOCHEMICAL PROCESSES

Abstract: The invention relates to an apparatus and a method for measuring NOx in biochemical processes, and to apparatus and methods for real time measuring the nitrification and/or denitrification rate of a liquid with or without suspended solids.

Description: APPARATUS AND METHOD FOR MEASURING NOx AND NITRIFICATION/DENITRIFICATION RATES IN BIOCHEMICAL PROCESSES Field of the Invention The present invention relates to apparatus and methods for measuring amounts of NO x (nitrate (NO 3 ) and/or nitrite (NO 2 )) and itrification/denitrification rates in liquid and controlling the treatment thereof. Background of the Invention Microorganisms used in sludge in industrial and municipal water treatment plants break down or degrade contaminants for the desired water treatment in these plants. Efficient process performance and control requires quick and accurate assessment of information on the activity of the microorganisms. This has proven to be a difficult task in view of the wide variety of materials and contaminants that typically enter into treatment systems. Also, variations in the quantity of wastewater being treated, such as daily, weekly or seasonal changes, can dramatically change numerous important factors in the treatment process, such as pH, temperature, dissolved oxygen, nutrients and the like, alteration of which can be highly detrimental to proper wastewater treatment. Improperly treated wastewater poses serious human health dangers. Various biological nutrient removal (BNR) processes are often used in biochemical systems/plants/processes. "BNR" is used hereinafter in a very generic sense, namely any biochemical process that uses microorganisms to remove nutrients. In BNR processes, contaminants in liquids such as wastewater, particularly carbon sources (measured as biochemical oxygen demand or BOD), ammonia, nitrates, phosphates and the like are digested by activated sludge in anaerobic, anoxic and aerobic (oxic) stages, also known in the art. In the anaerobic stage, wastewater, with or without passing through a preliminary settlement process, is mixed with return activated sludge (RAS), sometimes hereinafter referred to as "mixed liquor. " It is, of course, important to quantify the various contaminants in the wastewater. One of those contaminants that is important to quantify is the amount of NO x . This is because quantification of the amount of NO x provides valuable information about nitrification and denitrification processes. Also, it is important to determine the nitrification or denitrification rate to facilitate adjustment of various system parameters, such as retention time, to enhance the treatment process and increase treatment system efficiency in response to this important information. Summary of the Invention One aspect of the invention includes a method of measuring the nitrification rate for a liquid including isolating a first liquid sample at t 0 ; recording a value of ammonia [NH 3 ] j present in the first sample at a predetermined time r,; isolating a second liquid sample and introducing air into the second liquid sample after another predetermined time t 2 ; terminating the introduction of air into the second liquid sample and adjusting the pH of the second sample at t 3 ; recording another value of ammonia [7VH 3 ] 2 in the second sample at a predetermined time r 4 ; and determining the nitrification rate of the liquid according to the following formula: Δ[NH 3 ] NR = At wherein NR is the nitrification rate, At is t 2 -t 3 and Δ[NH 3 ] is [NH 3 ] r [NH 3 ] 2 . Another aspect of the invention includes another method of measuring a nitrification rate for liquids including isolating first and second liquid samples and introducing air into the second liquid sample at t 0 ; recording a value of ammonia [NH 3 ] ι present in the first sample and terminating introduction of air into the second sample at t, ; recording a value of ammonia [NH 3 ] 2 present in the second sample at t 2 ; and determining the nitrification rate of the liquid according to the following formula: Δ[NH 3 ] 7YR = At wherein NR is the nitrification rate, Δt is t x -t 2 and Δ[NH 3 ] is [NH 3 ] r [NH 3 ] 2 . The words "ammonia" ([NH 3 ]) and "ammonium" ([NH ]) are hereafter often used interchangeably regarding the concentration of ammonia in the aqueous phase. This is because at a given pΗ, there exists a chemical equilibrium between ammonia molecules and ammonium ions in the aqueous phase. This equilibrium is described in the following form with the equilibrium constant equal to one, at pH=9.25. NH 3 + H 2 0 » NH 4 + + OH The measurements of ammonia [NH 3 ] and ammonium [NH 4 + ] are substantially equivalent so long as the pH value of the solution is known. It is advantageous to measure ammonium concentration, [NH 4 + ], at a lower pH(pH < 6), while the measurement of ammonia concentration, [NH 3 ], is more convenient at an elevated pH(pH > 8) . The discussion of this invention often refers to the ammonia concentration as [NH S ] measured with an ammonia selective probe, with the understanding that at a lower pH, it can be replaced by [NH 4 + ] measured with an ammonium ion selective probe. The invention also includes a method of measuring NO x in liquids, especially wastewater. This method is different from other analyzing methods in that there is no need to prepare the sample by filtration or other method of solids removal. The method includes isolating a wastewater sample; adjusting the pH and/or ionic strength of the sample to a predetermined level for a predetermined time interval t,; recording a value of [NOJ ! present in the sample with an NO x selective probe(s); recording another value of [NO x ] 2 present in the sample after another predetermined time interval t 2 ; determining NO x concentrations in the sample at each predetermined time interval t, and t 2 according to the following formula: [NO x ] = 10 α ' mV+6 wherein a and b are linear coefficients of the ΝO x probe and mV reading is from the NO x ion selective probe(s); determining the changes in NO x according to the following formula: Δ[NO X ] = [NO X ] 2 - [NO X ], ; and determining the ΝΟ x concentration of the sample according to the following formula: Δ[NO X ] [NO X ] = [NO X ], . r, . Δt In yet another aspect of the invention, the rate of denitrification may be determined. The denitrification rate (DR) may be determined as follows: isolating a liquid sample at t 0 ; recording a value of [NOJ, present in the sample at a predetermined time tf, recording a value of [NO X ] 2 present in the sample at a predetermined time t 2 ; and determining the denitrification rate of the liquid according to the following formula: A[NO x ] DR = Δt wherein Δ[NO X ] is [NO ; - [NO X ] 2 and At = t 2 - t,. Description of the Drawings Fig. 1 is a schematic of a typical wastewater treatment process utilizing embodiments of the invention and shows the many locations that detectors can be installed through out the system. Fig. 2 shows a schematic front elevational view of an embodiment of apparatus of the invention used to monitor a bioreactor tank. Fig. 3 shows a schematic front elevational view of another embodiment of apparatus of the invention used to monitor a bioreactor tank. Fig. 4 shows an exploded schematic view, partially taken in section, of wastewater sampling apparatus in accordance with aspects of the invention. Fig. 5 shows an exploded schematic view, partially taken in section, of wastewater sampling apparatus in accordance with another embodiment of the invention. Fig. 6 shows a schematic view, partially taken in section, of solution dispenser apparatus in accordance with aspects of the invention. Fig. 7 is a block diagram of a method to measure ΝO x and a method of calibrating an NO x analyzer in accordance with aspects of the invention. Fig. 8 is a block diagram of a method of determining the rate of denitrification of wastewater. Fig. 9 is a block diagram of a method of determining the rate of nitrification of wastewater. Fig. 10 is a block diagram of another method of determining the rate of nitrification of wastewater. Detailed Description of the Invention In order to effectively control the operation of the BNR process, it is necessary to regulate specific process parameters based upon the biological activity of the microorganisms in the anaerobic, anoxic and/or oxic stages of the treatment. Wastewater treatment plants are often subjected to severe transient conditions, such as diurnal variations in organic loads. The proper evaluation and control of a BNR process requires an accurate and current assessment of the amount of NO x and ammonia in the mixed liquor, the nitrification rate and the denitrification rate, among other things, in a variety of environments and under a number of conditions. The apparatus for quantifying ammonia and/or NO x and/or nitrification rate and/or denitrification rate can be used in all stages of a WWTP or any combination thereof. Incorporation of the apparatus into a typical WWTP is shown schematically in Fig. 1. NO x and/or ammonia measurements may be taken at any point or location in the system shown in Fig. 1. This includes multiple measurement locations within a selected stage, if desired. The general application and use of the apparatus in the anaerobic, anoxic and/or aerobic stages of a typical wastewater treatment plant will now be discussed. One embodiment of apparatus for sampling wastewater is shown in Fig. 2. A bioreactor tank 1 (or, alternatively, a wastewater channel) contains wastewater 2 and/or sludge. Detection apparatus is mounted on the top of bioreactor tank 1 and extends into wastewater 2. The apparatus includes a central control and analysis unit 20 connected to optional computer/monitor 13 by wire or wireless connection 22. Similarly, central control and analysis unit 20 connects to detection probe 10 by way of wire connection 24. Motor container 26 also connects to central control and analysis unit 20 by way of connection wire 28. Power is supplied to motor container 26 also by wire connection 28. Detection probe 10 is positioned in detection chamber 8 and electrically connected to central control and analysis unit 20 to detect changes in the quantity of ammonia or ammonium or NO x concentration in wastewater samples depending on the configuration. At low pH, a preferred ammonium ion selective probe 10 is an ammonium probe manufactured by HACH or NICO. At mid-high pH a preferred ammonia detection probe 10 is an ammonia gas probe also manufactured by NICO or HACH. A preferred NO 3 and/or NO 2 ion selective probe(s) are manufactured by NICO. Of course, other apparatus can be employed as probes so long as the same or similar detection capabilities are available. Optional computer/monitor 13 may be of any suitable type such as a personal computer or the like. Device 52 consists of two containers (one storing ammonia or NO x calibration solution and the other storing pH adjustment solution and/or ionic strength adjustment solution) and a delivery device for each, for example, a pump. Device 52 is connected to central control and analysis unit 20 by wire 54. Device 52 provides ammonia or NO x calibration and pH adjustment solution and/or ionic strength adjustment solution to the liquid (e.g. wastewater) in detection chamber 8 by connection tube 53 through feed ports 55. The pH adjustment solution, typically a base for mid to high pH and an acid for low pH, may be selected from a wide variety of pH altering solutions. Bases include NaOH, KOH and the like. Acids include HCl, acetic acid and the like. The ionic strength adjustment solution, typically Al 2 (SO 4 ) 3 solution, or solution of Al 2 (SO 4 ) 3 , Ag 2 SO 4 , H 3 BO 3 , and sulfamic acid, can be selected from a wide variety of solutions for the adjustment of ionic strength of the wastewater sample. Device 52 is described in detail below in conjunction with Fig. 6. Sampling unit 11 is mounted onto a movable carriage 30 which is capable of moving substantially vertically upwardly and downwardly to move sampling unit 11 into and out of wastewater 2. The precise structure of movable carriage 30 is not critical so long as the preferred capability or movability of sampling unit 11 is achieved. Detection probe 10 has its detection end located in detection chamber 8. Detection chamber 8 has an opening 66 and an adjacent movable cover 32 which moves vertically upwardly and downwardly along guide channels 34 and closes or seals opening 66. Fig. 3 shows another embodiment of apparatus for sampling wastewater. The embodiment shown in Fig. 3 is similar to that shown in Fig. 2 except that apparatus providing for additional sampling capability is provided. Specifically, another detection chamber 8 having a probe 10 is mounted adjacent to the detection chamber/probe configuration shown in Fig. 2. Of course, additional connections are provided to the control and analysis unit 20 and solution supplied by device 52. Fig. 4 shows detection chamber 8 having a detection probe 10A with a detection end 50A. Detection probe 10A may be an ammonia, ammonium or an NO x detection probe. Detection chamber 8 also has an optional detection probe 10B with a detection end 50B. Optional detection probe 1 OB is a pH probe. Detection chamber 8 still further has feed ports 55 A and 55B. Feed device 52 feeds pH adjustment solution and/or ionic strength adjustment solution into detection chamber 8 through feed port 55B. Feed device 52 feeds ammonia or NO x to detection chamber 8 through feed port 55 A. Propeller 48 is located interiorly of detection chamber 8 and stirs or agitates samples when probes 10A and 10B are in operation. Cover 32 is in an open position which, when closed, covers opening 66. Propeller 48 is connected to motor container 26 by way of a series of coaxial tubes 102, 104 and 106. An adaptor 108 and a thrust bearing sleeve 112 are contained in and attached to middle tube 104. Outside tube 102 is mounted to base 101. Adaptor 108 is attached to threaded rod 110 to either open or close cover 32 depending on motor direction of linear actuator motor 116. Middle tube 104 travels axially only if induced drag on middle tube 104 exceeds an amount of torque required for linear actuator motor 116 to turn on threaded rod 110. This drag can be induced by propeller 48 attached to middle tube 104 and/or any bushings or other hardware in contact with middle tube 104. Thrust bearing sleeve 112 holds bearing 114 which carries axial tension of central tube 106 when cover 32 is closed. Bearing 114 allows middle tube 104 to rotate independently of central tube 106 and transfers axial motion of tube 104 to central tube 106. Outside tube 102 supports both base 101 and chamber 8 while protecting the internal parts. Chamber 8 is substantially sealed to outside tube 102 and when cover 32 is pulled against chamber 8 the space inside chamber 8 is sealed. When linear actuator motor 116 rotates in one direction threaded rod 110 travels downward, pushing cover 32 open. When nut 118 reaches thrust bearing 119, threaded rod 110 no longer travels axially and this causes middle tube 104 to substantially match the motor speed. Chamber 8 is then in an open condition and propeller 48 induces an exchange of fluid between the inside and outside of chamber 8. When linear actuator motor 116 rotates in the opposite direction, threaded rod 110 travels upward, pulling cover 32 closed. When chamber 8 is closed, axial motion of threaded rod 110 is prevented by tension on middle tube 104. This causes middle mbe 104 to rotate at the same speed as motor 116. Chamber 8 is then in a closed position so that fluid is retained inside chamber 8 while being constantly mixed by propeller 48. Fig. 5 shows another embodiment of a chamber 8 configuration containing an optional additional detection probe. All other components are the same as shown in Fig. 4. Optional detection probe 10C has a detection end 50. Optional detection probe 10C is a dissolved oxygen probe. It connects to central control and analysis unit 20 by way of connection 24C. Referring to Fig. 6, device 52 is constructed to accurately dispense various solutions to other components of the overall system. Device 52 includes a housing 198 and preferably contains two solution containers 200 and 202, although it may be configured to contain only one or more than two solution containers. The containers 200 and 202 have corresponding solution pumps 204 and 206 connected to their respective solution containers with pump feeding lines 208 and 210. The pump feeding lines are preferably equipped with a sharp or needle-type device 212 and 214 that extend though housing 198. Each solution container is preferably made of a plastic material that is pierceable by the needle or sharp device, whereby when the solution container is lowered onto the needle, it punctures the container to provide access to the solution. Most preferably, the container is shaped to urge liquid in the solution container to flow towards the needle device. Since it is important that the solutions remain uncontaminated and retain their precise concentration, for measurement purposes, it is important that they are sealed. However, in emptying the container, it is highly preferred to provide a means for air to fill in the space created in the container when solution is removed. This may be achieved by a number of means, although it is highly preferred to use needle-type device 216 and 218 to puncture solution containers 200 and 202 and provide air access to the interior of the solution containers. The needle-type device 216 and 218 are connected to air lines 230 and 232. Each pump 204 and 206 connected to the respective solution containers connects control and analysis unit 20 (not shown in Fig. 6), by line 222 and 224. The pumps 204 and 206 also connect to detection chamber(s) 8 (not shown in Fig. 6), by way of solution feeding lines 226 and 228 to supply the metered or precise quantity of solution to detection chamber(s) 8 at the specific time. Of course, the solution within the containers may vary. However, the preferred solution(s) are ammonium chloride or sodium nitrate. The pH and/or ionic strength adjustment solution(s) also can also be held in the containers . Other solutions may be utilized in accordance with the particular need. Solutions may, of course, be in various concentrations as needed. NO x is often a main part of the contaminants in wastewater. Therefore, a fast and easy method for real-time measurement of NO x in wastewater is highly advantageous. Accordingly, one aspect of the invention involves measuring the amount of NO x in the wastewater. This is performed by a method of measuring NO x in liquid including isolating a liquid sample; adjusting the pH and/or ionic strength of the sample at time r 0 ; recording a value of NO x present in the sample with an NO x selective probe(s) at a predetermined time t ; recording another value of NO x present in the sample after another predetermined time t 2 determining NO x concentrations in the sample at each predetermined time t, and t 2 according to the following formula: [NO x ] = 10 α ' mV+fc wherein a and b are linear coefficients of the NΟ x probe(s); determining the change in NO x in the sample according to the following formula: Δ[NO x ] = [NOJ 2 -[NO x ] ι; and determining the ΝΟ x concentration of the sample according to the following formula: This method is shown in the upper portion of the flow diagram shown in Fig. 7. The ΝΟ x analyzer can be calibrated according to the lower portion of the block diagram shown in Fig. 7 and according to the following method: a) Collect a mixed liquor sample from the wastewater treatment tank and conduct NO x analysis as described above, except that the sample is not discharged to the treatment tank after the NO x concentration is measured. Parameters and intermediate results such as [NOJ,, [NOJ 2 , mV,, mV 2 , Δ[NOJ/Δt are saved for use in the calibration step. b) After the ΝΟ x concentration is measured, a predetermined volume of nitrate or nitrite solution is injected into the sample container so that the concentration of NΟ x in the container increases by a Δ[NO x ] cl , (e.g. 0.5 ml of 1000 ppm ΝaΝΟ 3 or NaNΟ 2 solution for Δ[NOJ cl = 1 ppm, assuming the sampling chamber has a volume of 500 ml.) c) Wait to t 3 seconds to read the third mV reading from the probe [mV 3 ] . d) Inject a second dose of calibration solution so that the concentration of ΝΟ x increases by a Δ[NOJ c2 , (e.g. 2.0 ml of 1000 ppm ΝaΝΟ 3 or NaNΟ 2 solution for Δ[NOJ c2 =5 ppm, taken into account of the first dose of calibration solution.) e) Wait to t 4 seconds to read the fourth mV reading from the probe [mNJ. f) Use the following equations to calculate the linear coefficients of ΝΟ x , a and b: Δ[NOJ log [NOJo ~ — . (h - to) + Δ[NOJ cl = a • mV 3 + b Δt Δ[NOJ log [NOJo . ( - t ) + Δ[NOJ c2 = a • mV 4 + b At g) Use the newly obtained a and b to calculate [NOJ 0 from mV 0 . If the newly calculated [NOJ 0 substantially agrees with original [NOJ 0 , then the calibration is deemed successful, otherwise, use the newly calculated [NOJ 0 t0 repeat the calibration process. The calibration is considered complete when the difference between [NOJ 0 j and [NOJ 0 j+1 is within an acceptable, predetermined range. h) Discharge the sample to the treatment tank and start a new measurement cycle. i) The calibration of the NO x analyzer can be performed as frequently as every measurement cycle, or everyday. The default calibration frequency is preferably once a day. It is still further advantageous to determine the nitrification rate. There are two preferred methods to make such a determination in accordance with the invention. In a first embodiment, the method includes: a) isolating a first liquid sample at t 0 ; b) measuring the concentration of ammonia [NH 3 ] , or ammonium [NH ], present in the sample at a predetermined time t then releasing the first sample to the treatment tank; c) isolating a second liquid sample and introducing air into the second liquid sample after another predetermined time t 2 ; d) terminating the introduction of air into the second liquid sample and adjusting the pΗ of the second sample at r 3 ; e) recording another value of ammonia [NH 3 ] 2 or ammonium [NH 4 + ] 2 in the second sample at a predetermined time r 4 ; and f) determining the nitrification rate of the liquid according to the following formula: Δ[NH 3 ] Δ[NH 4 + ] NR = or NR = At At wherein NR is the nitrification rate, Δt is t t 2 and Δ[NH 3 ] is [NH 3 ]ι-[NH 3 ] 2 or Δ[NH ] is [NH ] r [NH ] 2 . This method is outlined in the flow diagram shown in Fig. 10. In the second embodiment which uses two sampling units (as shown in Fig. 3), the method includes: a) isolating first and second liquid samples and introducing air into the second liquid sample at t 0 ; b) measuring the concentration of ammonia [NH 3 ] , or ammonium [NH 4 + ] present in the first sample; c) terminating introduction of air into the second sample at t x ; d) measuring the concentration of ammonia [NH 3 ] 2 present in the second sample; and e) determining the nitrification rate of the liquid according to the following formula: Δ[NH 3 ] Δ[NH 4 + ] NR = or NR = Δt At wherein NR is the nitrification rate, At is t,-t 0 and Δ[NH 3 ] is [NH 3 ] 1 -[NH 3 ] 2 or Δ[NH ] is [NH ] r [NH ] 2 . This method is outlined in the flow diagram shown in Fig. 9. The preferred operation of the ammonia analyzer in the measurement mode is as follows: a) Collect a mixed liquor sample from the wastewater treatment tank. b) Inject pΗ adjustment solution to bring the pΗ of the water phase to about 12.0. This can be done either through a predetermined amount or feedback control by way of a pΗ probe. This is recorded as time zero, tg. c) Wait to t x seconds to read the first mV, reading from the ammonia probe. d) Wait to t 2 seconds to read the second mV 2 reading from the ammonia probe. e) Use the following equation to calculate ammonia concentrations from mN, and mV 2 , where a and b are linear coefficients of the ammonia probe. [NH 3 ] = \ ' mV+b f) The amount of released NH, from the sample is calculated as: Δ[NH 3 ] [NH 3 ] 2 - [NH 3 ], At t 2 - t x g) The ammonia concentration of the sample is calculated as: Δ[NH 3 ] [NH 3 ] 0 = [NH 3 ] , -. (t t 0 ) At h) After the measurement of ammonia concentration, the sample is discharged to the treatment tank, and a fresh sample is taken for the next analysis. The ammonia analyzer is preferably calibrated according to the following method: a) Collect a mixed liquor sample from the wastewater treatment tank and conduct ammonia analysis as described above, except that the sample is not discharged to the treatment tank after the ammonia concentration is measured. Parameters and intermediate results such as [NH 3 ], , [NH 3 ] 2 , mV,, mV 2 , Δ[NH 3 ]/Δt are saved for use in the calibration step. b) After the ammonia concentration is measured, a predetermined volume of ammonia solution is injected into the sample container so that the concentration of ammonia in the container increases by a Δ[NH 3 ] cl , (e.g. 0.5 ml of 1000 ppm ΝΗ 4 C1-Ν solution for Δ[NH 3 ] cl = l ppm, assuming the sampling chamber has a volume of 500 ml.) c) Wait to t 3 seconds to read the third mN reading from the probe (mV 3 ). d) Inject a second dose of calibration solution so that the concentration of ammonia increases by a Δ[NH 3 ] c2 , (e.g. 2.0 ml of 1000 ppm ΝH 4 C1-Ν solution for Δ[NH 3 ] c2 = 5 ppm, taken into account of the first dose of calibration solution.) e) Wait to t 4 seconds to read the fourth mV reading from the probe (mV 4 ). f) Use the following equations to calculate the linear coefficients of ammonia, a and b: Δ[NH 3 ] log [NH 3 ] 0 + . (t 3 - r 0 ) + Δ[NH 3 ] cl = a • mV 3 + b At Δ[NH 3 ] log [NH 3 ] 0 + . (t 4 - to) + Δ[NH 3 ] c2 = a • mV 4 + b At g) Use the newly obtained a and b to calculate [NH 3 ] 0 from mV 0 . If the newly calculated [NH 3 ] 0 substantially agrees with original [NH 3 ] 0 , then the calibration is deemed successful, otherwise, use the newly calculated [NH 3 ] 0 to repeat the calibration process. The calibration is considered complete when the difference between [NH 3 ] 0 j and [NH 3 ] 0 j+1 is within an acceptable, predetermined range. h) Discharge the sample to the treatment tank and start a new measurement cycle. The calibration of the ammonia analyzer can be performed as frequently as every measurement cycle, or everyday. The default calibration frequency is preferably once a day. It is also advantageous to determine the denitrification rate (DR). Determination of DR depends on the concentrations of NO x . It is calculated according to the method shown in the flow diagram of Fig. 8. The method includes: a) isolating a liquid sample at t 0 ; b) measuring the concentration of NO x ([NOJ,) present in the sample at a predetermined time t 7 ; c) measuring the concentration of ΝΟ x ([NOJ 2 ) present in the sample at a predetermined time t 2 ; and d) determining the denitrification rate of the liquid according to the following formula: Δ[NOJ DR = At wherein Δ[NOJ is [NOJ, - [NOJ 2 and At = t 2 - 1 } . One practical application of determining nitrification rate ΝR in the monitoring and control of wastewater treatment process is to evaluate and optimize the bioreactor 's operation. When ΝR is measured on a real time basis, the information will answer the following: 1) Whether the activated sludge has nitrification ability, i.e. the presence of nitrification bacteria in the biomass. A low or near zero ΝR value indicates that the nitrifier population in the biomass is low or does not exist, whereas a high value of ΝR indicates a proper nitrification process. 2) Under the current wastewater loading to the plant, to what degree has nitrification been achieved? When ΝR is determined, the required time for proper ammonia removal can be calculated based on the nutrient loading. This required nitrification time can be compared with the current hydraulic retention time in the bioreactor to see if proper nitrification can be achieved. 3) What is the best aeration rate to achieve the desired degree of nitrification? The optimal air supply rate can be reached when the air supply calculated from the ΝR value matches the true air demand in the nitrification process. Over-aeration will result in deterioration of biomass and wasted energy, while under aeration may cause improper treatment of the wastewater. Both cases can be avoided with proper aeration control with NR as one of control parameters. 4) What is the best mean cell residence time (MCRT) of the biomass in the bioreactor for the desired degree of nitrification? The population of nitrification bacteria can be estimated from the NR value. This estimation allows the operator to determine the proper mean cell residence time (MCRT) for the desired growth of nitrification bacteria in the biomass. The MCRT may be used to control the wasting of the activated sludge. 5) What level of biomass concentration needs to be maintained in the bioreactor to achieve nitrification? When the NR value is high, meaning a higher population of nitrification bacteria, the plant can afford to use a lower biomass concentration in the bioreactor to achieve nitrification, whereas a lower NR calls for maintaining higher biomass concentration in the bioreactor. 6) The NR measurement also allows the operator of the wastewater treatment plant to estimate how much wastewater influent the plant can treat with the existing facility, therefore planning for plant expansion or modification. Denitrification rate, DR, can be used in the monitoring and control of biological denitrification within the wastewater treatment process . When DR is measured on a real time basis, the information can answer the following: 1 ) What is the capacity of denitrification in the bioreactor? Based on the measured DR value, information on the nitrate loading to the anoxic zone, hydraulic retention time in the anoxic zone, and the desired degree of denitrification, one can estimate how much wastewater influent the plant can treat. 2) What is the optimal internal recycle rate to the anoxic zone? The nitrate loading to the anoxic zone fundamentally comes from the internal recycle of the nitrified mixed liquor at the end of the aerobic zone of a bioreactor, referring to Figure 1 for the location of denitrification internal recycle. Knowing the DR allows accurate control of the internal recycle, thus achieving full utilization of the anoxic zone and avoiding wasting pumping energy from over-recycling. 3) Is there any factor limiting the achievement of optimal denitrification? The DR measurement allows the evaluation of denitrification activity in terms of carbonaceous nutrient and nitrate loading. A lower DR indicates an endogenous denitrification, as carbonaceous nutrient is limited. Increased carbonaceous nutrient loading enhances the denitrification process. A higher DR, on the other hand, predicts an active denitrification process. Increasing the internal recycle improves the total nitrogen removal from the wastewater stream. The invention may be applied to any kind of microbial process including, but not limited to, wastewater purification (municipal, industrial and the like), pharmaceutical/biotechnology production, brewing, fermentation or any other process involving pure or mixed populations of micro organisms.

Claims: What is claimed is: 1. A method of measuring a nitrification rate for a liquid comprising: a) isolating a liquid sample at t 0 ; b) measuring the concentration of ammonia [NH 3 ] , or ammonium [NH 4 + ] X present in said sample at a predetermined time t λ ; c) isolating another liquid sample and introducing air into said another liquid sample after another predetermined time t 2 ; d) terminating said introduction of air into said another liquid sample and adjusting the pΗ of said another sample at t 3 ; e) measuring the concentration of ammonia [NH 3 ] 2 or ammonium [NH 4 + ] 2 in said another sample at a predetermined time r 4 ; and f) determining the nitrification rate of the liquid according to the following formula: Δ[NH 3 ] Δ[NH 4 + ] NR = or NR = Δt Δt wherein NR is the nitrification rate, Δt is t 3 -t 2 and Δ[NH 3 ] is [NH 3 ],-[NH 3 ] 2 or Δ[NH ] is [NH ] r [NH ] 2 . 2. The method defined in Claim 1 further comprising repeating steps a) - f) at selected intervals to determine changes in the nitrification rate. 3. The method defined in Claim 1 wherein said values of ammonia [NH 3 ] are determined with an ammonia selective probe. 4. The method defined in Claim 1 wherein said values of ammonium [NH 4 + ] are determined with an ammonium ion selective probe. 5. The method defined in Claim 3 further comprising periodically calibrating said ammonia selective probe. 6. The method defined in Claim 4 further comprising periodically calibrating said ammonium ion selective probe. 7. The method defined in Claim 1 wherein said liquid contains organic matter. 8. The method defined in Claim 7 wherein at least a portion of said organic matter is capable of releasing ammonia. 9. The method defined in Claim 1 wherein said liquid is unfiltered. 10. The method defined in Claim 1 wherein said liquid is wastewater. 11. A method of measuring a nitrification rate for liquids comprising: a) isolating first and second liquid samples and introducing air into said second liquid sample at t 0 ; b) measuring the concentration of ammonia [NH 3 ] , or ammonium [NH 4 + ] X present in said first sample; c) terminating introduction of air into said second sample at t,; d) measuring the concentration of ammonia [NH 3 ] 2 or ammonium [NH 4 + ] 2 present in said second sample; and e) determining the nitrification rate of the liquid according to the following formula: Δ[NH 3 ] Δ[NH 4 + ] NR = or NR = Δt Δt wherein NR is the nitrification rate, Δt is t x -t 2 and Δ[NH 3 ] is [NH 3 ] r [NH 3 ] 2 or Δ[NH ] is [NH ] r [NH ] 2 . 12. The method defined in Claim 11 further comprising repeating steps a) - d) at selected intervals to determine changes in the nitrification rate. 13. The method defined in Claim 11 wherein said values of ammonia are determined with an ammonia selective probe. 14. The method defined in Claim 11 wherein said values of ammonium are determined with an ammonium ion selective probe. 15. The method defined in Claim 13 further comprising periodically calibrating said ammonia selective probe. 16. The method defined in Claim 13 further comprising periodically calibrating said ammonium ion selective probe. 17. The method defined in Claim 11 wherein said liquid contains organic matter. 18. The method defined in Claim 17 wherein at least a portion of said organic matter is capable of releasing ammonia. 19. The method defined in Claim 11 wherein said liquid is unfiltered. 20. The method defined in Claim 11 wherein said liquid is wastewater. 21. A method of measuring NO x in liquid comprising: a) isolating a liquid sample; b) adjusting the pH and/or ionic strength of said sample at time c) recording a value mV l present in said sample with an NO x selective probe at a predetermined time /,; d) recording another value mV 2 present in said sample after another predetermined time t 2 ; e) determining NO x concentrations in said sample at each predetermined time t, and t 2 according to the following formula: [NOJ = 10 α "" v+6 wherein a and b are linear coefficients of the ΝΟ x probe; f) determining changes in NΟ x in said sample according to the following formula: Δ[NOJ = [NOJ 2 -[NOJ, ; and g) determining the ΝΟ x concentration of the sample according to the following formula: Δ[NOJ [NOJ 0 =[NOJ 1 . (t t Q ) , At wherein Δt is t 2 - t 22. The method defined in Claim 21 further comprising discharging said sample and repeating steps a) - g). 23. The method defined in Claim 21 further comprising periodically calibrating said nitrate and/or nitrite selective probe. 24. A method of measuring a denitrification rate for a liquid comprising: a) isolating a liquid sample at t 0 ; b) measuring the concentration of [NOJ , present in said sample at a predetermined time t , c) measuring the concentration of [NOJ 2 present in said sample at a predetermined time t 2 ; and d) determining the denitrification rate of the liquid according to the following formula: Δ[NOJ DR = , At wherein Δ[NOJ is [NOJ, - [NOJ 2 and At = t 2 - t,. 25. The method defined in Claim 24 further comprising steps a) - d) at selected intervals to determine changes in the denitrification rate. 26. The method defined in Claim 24 wherein said values of [NOJ are determined with a nitrate and/or nitrite selective probe. 27. The method defined in Claim 24 wherein said liquid is wastewater.

Inventors: KOLB MARCUS E, LEE JAW FANG, MANESHIN SERGEY K, YANG XIN, KOLB, MARCUS, E., LEE, JAW, FANG, MANESHIN, SERGEY, K., YANG, XIN
Applicants: BIOCHEM TECHNOLOGY INC, BIOCHEM TECHNOLOGY, INC.
Application year: 1999
Main classification: G01N33
IPC codes: C02F1, C02F3, G01N1, G01N27, G01N33