WO2013079801A1 - Method and device for monitoring and controlling the state of a process stream - Google Patents

Method and device for monitoring and controlling the state of a process stream Download PDF

Info

Publication number
WO2013079801A1
WO2013079801A1 PCT/FI2012/051190 FI2012051190W WO2013079801A1 WO 2013079801 A1 WO2013079801 A1 WO 2013079801A1 FI 2012051190 W FI2012051190 W FI 2012051190W WO 2013079801 A1 WO2013079801 A1 WO 2013079801A1
Authority
WO
WIPO (PCT)
Prior art keywords
measuring
stream
process stream
sample
dissolved oxygen
Prior art date
Application number
PCT/FI2012/051190
Other languages
French (fr)
Inventor
Marjatta Piironen
Iiris Joensuu
Pekka ILMOLA
Kaj Jansson
Original Assignee
Kemira Oyj
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kemira Oyj filed Critical Kemira Oyj
Priority to US14/362,135 priority Critical patent/US9970919B2/en
Priority to CA2857383A priority patent/CA2857383C/en
Priority to CN201280059316.7A priority patent/CN103959059B/en
Priority to EP12816314.4A priority patent/EP2786136B1/en
Priority to ES12816314T priority patent/ES2741651T3/en
Priority to BR112014013342-5A priority patent/BR112014013342B1/en
Publication of WO2013079801A1 publication Critical patent/WO2013079801A1/en

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/34Paper
    • G01N33/343Paper pulp
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/18Water
    • G01N33/1826Organic contamination in water
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M1/00Apparatus for enzymology or microbiology
    • C12M1/34Measuring or testing with condition measuring or sensing means, e.g. colony counters
    • C12M1/3446Photometry, spectroscopy, laser technology
    • C12M1/3461Bio- or chemi-luminescence
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12QMEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
    • C12Q1/00Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
    • C12Q1/02Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
    • C12Q1/04Determining presence or kind of microorganism; Use of selective media for testing antibiotics or bacteriocides; Compositions containing a chemical indicator therefor
    • C12Q1/06Quantitative determination
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/18Water
    • G01N33/1806Biological oxygen demand [BOD] or chemical oxygen demand [COD]
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/483Physical analysis of biological material
    • G01N33/487Physical analysis of biological material of liquid biological material
    • G01N33/48707Physical analysis of biological material of liquid biological material by electrical means
    • G01N33/48735Investigating suspensions of cells, e.g. measuring microbe concentration
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/20Controlling water pollution; Waste water treatment

Definitions

  • the present invention concerns a method and device for monitoring and optionally controlling the microbiological state in process streams based on the measurement of variables, such as dissolved oxygen or rH or both, optionally assisted by soft sensors, based e.g. on Linquistic Equations (LE).
  • variables such as dissolved oxygen or rH or both
  • soft sensors based e.g. on Linquistic Equations (LE).
  • a common problem in many industrial process systems e.g. in paper and pulp processing systems, is microbial growth, if microbes are not controlled efficiently. Microbiological growth may cause several problems in the systems.
  • the bacteria in a process stream may cause spoilage of the stream or bacteria may attach to system surfaces forming biofilm or slime.
  • biofilm masses that detach from system surfaces can be carried into the pulp waters and formed into the paper sheet thereby weakening the formed paper sheet quality, e.g. by causing it to tear or causing holes in the paper.
  • process stages are ideal for the development of microbes, whereby there may be an increase in the microbial content of said streams.
  • Other examples of locations ideal for microbiological growth in a process system are dead zones of process systems (e.g. poor mixing zones).
  • microbe analyses are presently carried out in the laboratory due to the lack of fast online measuring methods and devices.
  • the methods e.g. plate count, are time-consuming and it can take up to 2-3 days to get the results of the analysis.
  • the result may be an inadequate biocide dosage to the process stream and, thus, a poor paper quality as well as a poor cost-efficiency of the process.
  • biocides to maintain a low level of microbes in a process stream.
  • WO 2008/101089 describes a method of monitoring microbiological activity under aerobic conditions in process streams based on changes on dissolved oxygen concentrations measured using specified process steps.
  • the measurement is claimed not to be suitable for process streams of low dissolved oxygen concentration.
  • the process is complex, requiring cleaning of the measuring probes between measurement points during measurement cycles.
  • microbiological state herein is referred to the activity of all such microorganisms that can influence the dissolved oxygen concentration and/or the rH value in a process stream, and optionally to aerobic or anaerobic conditions in a process stream.
  • the idea is based on measuring parameters, such as the concentration of dissolved oxygen, and/or the rH, in a process stream.
  • a sample is taken batch-wise from the process to a measuring unit and concentration of dissolved oxygen in the sample and/or rH of the sample is measured during a measuring cycle.
  • the temperature is preferably also measured, as a more precise value for the concentration of dissolved oxygen can then be obtained.
  • soft sensors based on any equation(s) and/or model(s), e.g. on Linquistic Equation (LE) models are preferably used to assist in the interpretation of the measurement data and/or calculated result data.
  • other process data obtained by any known sensors or analyzers may be utilized to give an even more accurate perception of the microbiological state of the process streams for monitoring and optionally controlling the microbiological state of a process stream.
  • the present invention concerns a method and a device for monitoring and optionally controlling the microbiological state in a process stream by measuring the concentration of dissolved oxygen or the rH value, or both, in said stream.
  • the device of the present invention is characterized by what is stated in Claim 13 and the uses of the present invention are characterized by what is stated in Claims 19 and 20.
  • This method and device make it possible to monitor the microbiological state of a process stream, in particular industrial stream, and to optionally control the microbiological state.
  • the microbiological state can be controlled by controlling, preferably automatically, the amount of biocide(s) and/or location of the dosing of biocide(s) and/or selection of the type of biocide(s) to be added to the process stream, with a simple measurement method.
  • the method allows also analysis of process streams with low concentration of dissolved oxygen. It also enables monitoring and optionally controlling the microbiological state of a process stream under anaerobic conditions.
  • the method and the device may provide online data on the microbiological state of the analyzed process stream.
  • Figure 1 is a schematic picture of an arrangement to perform an embodiment of the method according to the invention.
  • Figure 2 is a graphical illustration of exemplary outputs of the online-measurement device of the present invention, showing the concentration of measured dissolved oxygen in the measurement unit and the temperature.
  • Figure 3 is a graphical illustration of the relative oxygen consumption and the amount of aerobic bacteria in an exemplary pulp suspension.
  • Figure 4 is a graphical illustration of the oxygen consumption (mg/1) and the relative oxygen consumption (%) of an exemplary pulp sample between ti and t 2 in the measuring cycle.
  • Figure 5a is a graphical illustration of the relative oxygen consumption and the oxygen consumption in an exemplary pulp sample at different moments of time during a measurement.
  • Figure 5b shows the relative oxygen consumption and the amount of aerobic bacteria in the same exemplary pulp suspension.
  • Figure 6 is a graphical illustration of the amount of microbes in an exemplary pulp suspension, as measured using a conventional laboratory analysis method and estimated using a soft sensor based on linquistic equations.
  • Figure 7 is a graphical illustration of the effect of the pH on the redox value, as well as rH values corresponding to different process conditions, e.g. aerobic or anaerobic conditions.
  • Figure 8 is a graphical illustration of the amount of microbes at different rH values, Figure 8a showing a measured rH values over a period of time, where the number of aerobic bacteria increases as the rH value decreases, and Figure 8b showing the measured rH value versus amount (CFU) of anaerobic bacteria measured in the laboratory.
  • Figure 9 is a schematic picture of an exemplary control strategy based on measurement(s) according to the present invention in a suspension stream intended to undergo a two-step biocide treatment, with two separate addition points.
  • Figure 10 is a schematic picture of an exemplary control strategy (for a basic feedback FB controller) based on measurement s) according to the present invention in a suspension stream intended to undergo a one-step biocide treatment.
  • Figure 11 is a schematic picture of an exemplary control strategy (for an FB controller with a cascade loop) based on measurement s) according to the present invention in a suspension stream intended to undergo a one-step biocide treatment.
  • the present invention concerns a method and device for monitoring, and optionally controlling the microbiological state, of a process stream preferably of an industrial process by batchwise obtaining a sample of the suspension stream, measuring the concentration of dissolved oxygen or the rH value, or both, in said stream at least at two time points, calculating the relative oxygen consumption, the change of rH or the relative change of the rH, between two of said two or more time points, or calculating two or more of these, and determining microbiological state of the stream based on the measurements, and an device suitable for use in implementing said method.
  • microbiological state of a process stream is referred to the activity of all such microorganisms that can influence the dissolved oxygen concentration and/or the rH value in a process stream, and optionally to aerobic or anaerobic conditions in a process stream.
  • Microbiological activity in process streams can be indirectly measured by monitoring the consumption of dissolved oxygen because dissolved oxygen consumption is directly related to aerobic metabolism of the cell.
  • the relative dissolved oxygen consumption can be used to monitor microbiological state of a process stream. Relative dissolved oxygen consumption was found to be a very sensitive measurement for microbiological activity in accordance with the method of the invention in the aerobic conditions (i.e. when the concentration of dissolved oxygen is higher than 0 mg/1). Often the relative consumption of dissolved oxygen correlates also with the amount of the aerobic bacteria.
  • the rH value or especially the change or relative change thereof was found to describe microbiological activity under anaerobic and anoxic conditions. Under anaerobic and anoxic conditions microbes generate such products which tend to decrease rH value of the process stream. The rH value, change or relative change thereof often also correlates with the amount of anaerobic bacteria.
  • rH value may correlate also in aerobic conditions with the amount of the aerobic bacteria in the suspension stream to be analyzed, especially when strongly oxidative chemicals are substantially absent in the sample.
  • the oxygen concentration is decreased and thereby the rH value decreases.
  • microbiological state combining information from the initial values of the measurement cycles or dissolved oxygen concentration and/or rH with one or more of change of rH, relative change of rH or relative change in oxygen consumption,
  • microbiological state of a process stream can be monitored, optionally controlled with the meathod of the invention both under aerobic and anaerobic conditions. This is especially preferred to be used in a process where the process conditions vary between anaerobic and aerobic process conditions.
  • the device according to the invention contains a measuring unit 10 with an inlet 23 and an outlet 24, means for measuring amount of dissolved oxygen 6 and/or means for measuring rH 7 within the measuring unit, with reference to Figure 1.
  • the device preferably contains an inlet conduit 11 for directing a sample to the measuring unit 10.
  • the device may contain an outlet conduit 12 for directing the sample from the measuring unit.
  • the inlet conduit 11 is in connection with a process line 13 whereby the inlet conduit allows taking a side-draw from the main process line 13.
  • the said means 7 for measuring the rH value preferably includes: means 7a for measuring the redox potential, means 7b for measuring the pH value and preferably means 7c for calculating the rH value.
  • the device includes means 8 for measuring the temperature and optionally means 9 for measuring pressure.
  • the device of the present invention is suitable for monitoring, optionally controlling, the microbiological state in a process stream by measuring online the amount of dissolved oxygen or the rH, or both, in said stream.
  • the device is in fluid connection with a process line 13 for a process stream.
  • Process line 13 is equipped with a side draw 25 which may be the inlet conduit 1 1 for withdrawing a sample from said process stream, preferably a main process stream.
  • the side draw 25 functions as a sampling point.
  • the side draw 25 is in fluid connection with a measuring unit 10.
  • the measuring unit is preferably a closed vessel with openings for entrance(s) of the sample flow, exit(s) of the sample, and any opening(s) for process equipment if needed, e.g. measuring probes or sensors, inlets for water or gas lines.
  • Side draw 11 is preferably equipped with valve VI for sampling from process line 13.
  • the vessel 10 is preferably lacking means for mixing the sample during the
  • the measuring unit 10 is intended for holding the sample during the measurement.
  • the measuring unit may contain an inlet 14 with valve V4 for pressurized air to provide turbulence to the process stream between any chosen measurement cycle, thereby enabling cleaning of surfaces inside the measuring unit.
  • the cleaning of the surfaces inside the vessel may additionally or alternatively be effected by providing water via inlet line 17 for washing water, including valve V5.
  • the device contains flow inlets only for the entrances of the sample flow to be measured.
  • the device comprises means either for measuring the concentration of dissolved oxygen 6 or for measuring the redox 7a and pH 7b to determine rH of the sample within said measuring unit 10, or both 6, 7, as well as means 20 for processing the measurements and performing calculations based on the measured values (e.g. calculating relative dissolved oxygen consumption, rH, change or relative change of rH).
  • the optional means 7 for measuring the rH of the sample preferably include means 7a for measuring the redox potential of the sample and means 7b for measuring the pH value of the sample, and preferably means 7c for calculating the rH value of the sample, and optionally means for measuring temperature.
  • the above mentioned means 6 for measuring the concentration of dissolved oxygen are preferably selected from (non-electrochemical) sensors not requiring the use of
  • the device preferably comprises also means 8 for measuring the temperature of the sample within said measuring unit 10, and preferably also means 9 for measuring the pressure within said measuring unit 10.
  • the means 8 for measuring the temperature are particularly preferred when applying the means 6 for measuring the concentration of dissolved oxygen.
  • These means 6 may include separate means for measuring the temperature, such as a temperature sensor or a thermometer.
  • the means 8 for measuring the temperature are particularly also preferred when applying the means 7 for measuring the rH.
  • the measuring unit may thus include means for measuring temperature of the sample within the vessel.
  • means 6 for measuring the concentration of dissolved oxygen and/or means for measuring rH of the sample may include additional means for measuring temperature.
  • the device means 19 for controlling and monitoring the function of the device. This control and/or monitoring can take place on site or using a remote system.
  • These means 19 are used, among others, for controlling the cycles and sequences of cycles, for temperature control, for controlling the calculations (e.g.
  • the device further comprises means 21 for calculating the amount of biocide to be added into the process line 13, and means 22 for dosing said biocide into the process line 1.
  • the device includes a temperature controlled measurement vessel 10, inlet conduit 11 and washing line 15 with supplementary equipment, e.g. to regulate the flows in said lines (e.g valves VI, V2, V6), as well as a control unit 19. Since dissolution of oxygen in liquid e.g. water depends on the temperature, the temperature of the measurement reactor 10 is monitored and optionally controlled. The heating and/or the cooling of the measuring unit 16, that are required if the measurements are run at constant temperature, are realized using, e.g.
  • a sampling system comprises at least an inlet conduit 11, at least means (e.g. valve(s)) to regulate the sample flow between a process stream 13 and a measuring unit 10, and preferably an outlet conduit 12.
  • a sampling line washing comprises at least a washing line 15 and at least means to regulate the washing water flow (e.g. valve V6 and VI) between a process stream 13 and a washing line 15.
  • the pressure of the measuring unitlO is monitored and optionally controlled. Measurements of the dissolved oxygen and/or rH are preferably carried out in the normal air pressure. Normal air pressure can be obtained into the measurement vessel by opening valve V3 of the outlet conduit (12) before the measurement starts or by having the outlet conduit open to the normal pressure. In a preferred embodiment the V3 is not in the system.
  • the means 20 for processing the measurements and performing calculations based on the measured values, means 19 for controlling and monitoring the function of the device and means for 21 for calculating the amount of biocide(s) are included in a same system, e.g. programmable logic and/or industrial PC.
  • a preferred device includes a measuring unit, online-sensors, sampling line washing, sampling systems, and programmable logic and/or industrial PC for processing the measurement results, controlling and monitoring the function of the device and for calculation the amount of biocides to be added into the process line.
  • the measured and/or calculated values according to the invention may be monitored locally or via a remote system, e.g. web-based.
  • the method of the present invention for monitoring the microbiological state, in a process stream includes the steps of
  • microbiological state in a process stream by measuring the concentration of dissolved oxygen or the rH, or both, in said stream, the method comprising
  • the calculated values include calculating relative oxygen consumption, or change of rH or relative change of the rH, or rate of the change of rH or consumption of dissolved oxygen between two of said two or more time points, or calculating two or more of these.
  • the determined microbiological state in said stream is used to optimize the biocide program, e.g. to select a biocide or biocides and/or calculate an amount or dose of biocide(s) to be added into the process stream and/or to select the location of the addition point(s) of the biocide(s). It can also be used to identify the location and/or source of microbiological problems in a system of which the process stream is a part of, such as pulp, broke, water circulation and raw water, which can be present in, e.g. tanks, containers, pulpers and pipes.
  • the determined microbiological state in said stream is used to control, preferably automatically, the microbiological state of the process stream by controlling the amount of biocide(s) added to the process stream, the selection of points of addition, or selection of the type of biocide(s) or any combination of the three.
  • the controlling of microbiological state in said stream includes controlling the amount of biocide(s) added to the process stream, preferably by an automated control system.
  • controlling of microbiological state in said process stream by adding an amount of biocide(s) to the process stream, preferably by an automated control system.
  • the broke tank where the broke can be stored for long periods of time, such as 2-1 Oh, or even days.
  • the determined microbiological state may also be used to determine and control the desired delay time of process streams, such as the broke of a paper or board manufacturing process, in various tanks, since a shorter delay time might be required, for example, if there is a large increase in the microbe growth within said tank.
  • the device according to the invention is used in the implementation of this method.
  • the process stream to be analyzed may be any aqueous or non-aqueous liquid, optionally comprising solid matter.
  • the solid matter can be in suspended and/or colloidal form.
  • the process stream is particularly a process stream in a water circulation system of an industrial process, any aqueous suspension, such as paper or board pulp, wastewater, paper coating colour, activated sludge, inorganic sludge, or washing streams, such as the ones used in oil drilling or mining.
  • the process stream may originate from an industrial water system or municipal water system.
  • the stream consists of paper or board pulp suspension including optional additives.
  • a process stream may be a flow or a stream in a process or stagnant, e.g. sample or content of a storage tank.
  • batch-wise sampling is used.
  • a process stream is conducted to a measuring unit.
  • the measuring unit is filled with the process stream sample, the flow is interrupted to keep the sample in the measuring unit.
  • the sampling is usually performed conducting a process stream through the measuring vessel for a period of time (sampling time) to obtain a representative sample.
  • sampling is interrupted to keep the sample in the measuring unit.
  • the sample is kept in the measuring unit for a period of time, i.e. a measuring cycle.
  • Measurements are performed at least at two time points during a measuring cycle.
  • the time used for the measuring cycle is evaluated based on the general (average)
  • the measuring cycle varies between 1 minutes and 3 hours, more preferably between 15 minutes and 2 hours.
  • An example of the output of measurements is shown in Figure 2.
  • the sampling time was 15 s and measuring cycle of dissolved oxygen was 2 h.
  • the measurements are performed during the whole measuring cycle, e.g. a measurement value is recorded 60 times per minute during the measuring cycle, e.g. during two hours.
  • the values measured (concentration of dissolved oxygen or a combination of pH and redox potential, or both of these) at least at the two time points are used to calculate the oxygen consumption (ADO), the relative oxygen consumption (ADO%), rH value (rH), the change of the rH value ( ⁇ ) and/or the relative change of the rH value ( ⁇ %).
  • the oxygen consumption (mg/1) is calculated using equation (1):
  • ADO% 100% ⁇ 0 2 ( ⁇
  • 0 2 (ti) where 0 2 (ti) is the first value of the concentration of dissolved oxygen.
  • the first value is preferably measured at the beginning of the measuring cycle, e.g. within the first 15 minutes thereof.
  • 0 2 (t 2 ) is the second value of the concentration of dissolved oxygen.
  • the second value is preferably measured at the end of the measuring cycle, e.g. within the last 15 minutes of the measuring cycle.
  • the redox value is pH dependent.
  • the change of the rH value can be calculated using the following equation (5):
  • ArH rH( tl ) - rH(t 2 ) (5) and the relative change of the rH value (%), using the following equation (6): where rH(ti) is the first rH value. First rH value is preferably measured at the beginning of the measuring cycle, e.g. within the first 15 minutes thereof. rH(t 2 ) is the second rH value and measured after the first value. The second rH value is preferably measured at the end of the measuring cycle, e.g. within the last 15 minutes thereof.
  • the method and device of the present invention allow also online monitoring of the measured rH value and/or concentration of dissolved oxygen (as shown in Figure 2) during a measurement cycle.
  • the rate of oxygen consumption and/or rate of rH change may also be used for selecting time period suitable for the measurement cycle and/or monitoring the microbiological state of the process stream.
  • the method is preferably carried out using a sequence of cycles, the cycles including at least one sampling cycle and at least one measuring cycle, preferably consisting of one sampling cycle and one measuring cycle.
  • sampling cycle is usually shorter than the measuring cycle.
  • Sampling time depends on the process, and may be e.g. between 60 seconds and 2 minutes. A suitable sampling time can be determined by a person skilled in the art. There can also be a time period between the cycles (after one sampling and measuring cycle has ended), e.g. if it is enough to receive monitoring data of the process stream only some times per day.
  • a process stream is conducted to a measuring unit without interrupting the process flow, and the rH value of the process flow is measured during the flow.
  • the rH value is used to monitor, optionally control, the microbiological state of the process flow. It is preferred to utilize this embodiment especially for inorganic sludges, such as coating colors.
  • Figure 8b show that rH value as such correlates with amount of anaerobic bacteria. rH may also correlate with amount of aerobic bacteria in some process streams, as shown in Figure 8a. However, in case of changes in the process flow other than microbiological, the rH value as such may not provide information on the microbiological state alone.
  • the temperature of the sample and optionally the pressure in the measuring unit is measured.
  • This is particularly useful when determining the microbiological state of the sample using the concentration of dissolved oxygen, as the dissolution of oxygen into liquid, e.g. water is temperature dependent and also pressure dependent.
  • the method can either be carried out at constant temperature, or the measured temperature can be included in the subsequent calculations to compensate for any changes in the temperature. The same applies for the pressure in the measuring unit during the
  • the concentration of dissolved oxygen or the rH value is used for determining the microbiological state of the process stream.
  • concentration of dissolved oxygen is higher than about 0 mg/1
  • concentration of dissolved oxygen in the sample is preferred to measure concentration of the dissolved oxygen in the sample and use relative consumption of dissolved oxygen to determine the microbiological state of process stream.
  • concentration of dissolved oxygen is about 0 mg/1
  • rH value of the sample is preferred to measure rH value of the sample and use change or relative change of rH to determine the microbiological state of process stream.
  • both concentration of the dissolved oxygen and the rH value are measured.
  • the initial value(s), preferably value(s) measured at the beginning of the measuring cycle, of dissolved oxygen concentration and rH describe whether the process conditions are anaerobic or aerobic and may be used for selecting of the at least one measurement (dissolved oxygen or rH) used for determining the microbiological state.
  • measurement of initial value(s) of the concentration of dissolved oxygen or the rH is carried out at the beginning of or before (e.g. during the sampling) the measurement cycle to determine whether the process stream conditions are aerobic or anaerobic.
  • the results obtained in this initial measurement s) are preferably interpreted and used in selecting, preferably automatically, a suitable measurement parameter from the concentration of dissolved oxygen, the rH or their combination for a measurement cycle, preferably current or next, or any following measuring cycle, and optionally used to control the microbiological state of the process stream.
  • Carrying out initial measurement of the concentration of dissolved oxygen or the rH at the beginning of the measurement cycle may be effected by analyzing one or several initial measurement values at the beginning of a measurement cycle, e.g. within the first 60 seconds of the measurement cycle. Thereby the suitable measurement parameter from the concentration of dissolved oxygen, the rH or their combination can be selected for the ongoing measurement cycle.
  • the initial value can also be the value, first value, which is used in the calculations of change of rH, relative change of rH and/or relation oxygen consumption change.
  • the measurement takes place online, as this makes it possible to react to the effects of temporary changes in the microbiological state of the analyzed stream.
  • concentration of dissolved oxygen in the process stream and/or the rH in the process stream can also be measured before taking the sample to or before it searches a measuring unit or during the process stream flows through the measuring unit.
  • One or more of the said measurements obtained outside the measurement cycle can be used for monitoring, optionally controlling the microbiological state of the process stream as such or in combination with the calculated values obtained from the measurements outside the measuring cycle.
  • Figure 3 shows relative oxygen consumption values determined with a method according to the invention vs. amount of aerobic bacteria on the sample, measured using the plate count method. When amount of microbes is high, the relative oxygen consumption during the measuring cycle is high. When the amount of microbes is low the relative oxygen consumption is small.
  • Oxygen can be consumed also by chemical oxidation reactions or oxygen can be released in chemical reactions (e.g. decomposition of H 2 0 2 ). Chemical reactions have strongest effect immediately after chemical addition and usually require presence of strong oxidants. The effect of chemical reactions on the estimation of the microbiological state of a process stream can be taken into account or eliminated by selecting the measurement or sampling location. A person skilled in the art is capable of taking this into account.
  • the rH value of a process stream can be affected by changes in a process stream other than microbiological changes, such as changes in the bleaching of process flow or addition of strong oxidative chemicals.
  • changes in a process stream other than microbiological changes such as changes in the bleaching of process flow or addition of strong oxidative chemicals.
  • Figure 4 shows examples of two measuring cycles where concentration of the dissolved oxygen (mg/1) in the sample was recorded.
  • the first value at the beginning of measuring cycle is 6 mg/1 and the second value at the end of measuring cycle is 5 mg/1.
  • Oxygen consumption during the measuring cycle is thus 1 mg/1 and relative oxygen consumption 17 %.
  • the first value at the beginning of measuring cycle is 1 mg/1 and the second value in the end of measuring cycle is 0 mg/1.
  • Oxygen consumption during the measuring cycle is 1 mg/1 and relatively oxygen consumption 100 %.
  • the overall level of the concentration of the dissolved oxygen is high and the oxygen consumption as well as the relative oxygen consumption is quite low. This indicates that the microbiological activity is low and amount of bacteria is low whereby the microbiological state is good.
  • the high relative oxygen consumption indicates poor microbiological state probably resulting from high activity of aerobic bacteria.
  • the oxygen consumption is the same 1 mg/1.
  • relative oxygen consumption in the two examples differs significantly.
  • Figure 5a is a graphical illustration of the relative oxygen consumption and the oxygen consumption in a pulp process stream as a function of time.
  • Figure 5b shows the relative oxygen consumption and the amount of aerobic bacteria in the same exemplary process stream. The values of the oxygen consumption and relative oxygen consumption are obtained from sequential measurement cycles. In the results, Figure 5a shows a significant change in the relative oxygen consumption (%) as a function of time while the oxygen consumption (mg/1) remains nearly unchanged. Figure 5b shows that a significant change occurs also in the amount of aerobic bacteria. Thus, relative oxygen consumption may be used to give reliable information of the microbiological state of the process stream.
  • any known surface fouling sensors or analyzers may be utilized to give additional information of the microbiological quality of the process streams.
  • Soft sensors are preferably implemented in the method according to the invention.
  • Soft sensors are additional estimation systems utilizing calculations to provide more detailed results of the microbiological state of a process.
  • Soft sensors e.g. based on Linquistic Equation (LE) models are preferably used to assist in the interpretation of measurement or calculated data, particularly in the method step of determining the microbiological state of the suspension, by providing equations used in calculations.
  • the said data may be data obtained according to the method of the invention or other process measurements obtained by any known sensors or analyzers. For example the amount of microbes after chemical treatment can be predicted on the basis of the rH value and the amount of biocide residual using a soft sensor.
  • the results of a soft sensor may be used as such or in combination with the method according to the invention to monitor, and optionally control the
  • microbiological state of a process stream An exemplary result of a model based on soft sensors is shown in Fig. 6, as compared to the results of a laboratory analysis.
  • the method further comprises controlling the microbiological state in said process stream by adding an effective amount of biocide(s) to the process stream, preferably by an automated control system.
  • feedforward (FF), feedback (FB) control and/or FB controller with a cascade loop are used for controlling the microbiological state of the said process stream.
  • the measurements for the determination of the microbiological state according to the invention can be carried out on a sample of the process stream taken either before the stream reaches a point of biocide dosing in the process stream, or after this point.
  • the output(s) of the method according to the invention can be used in dosing control of biocides (amount, type of, location).
  • the sample is taken before the stream reaches the biocide dosage point, and the results are used to control the subsequently required amount of biocide dose to be added to the process stream (i.e. feedforward (FF) control in Fig. 9).
  • the sample is taken after the biocide has been added, and the results are used to determine the success of the biocide treatment. Also in the latter case, the results may be used to control the required amount of biocide dose (i.e. feedback (FB) control, Fig. 10).
  • FB feedback
  • samples are taken from the stream both before and after two points of biocide dosage as shown in Fig 9.
  • a feedforward as well as a feedback control of the required amount of biocide addition.
  • the said points of biocide dosages may dose the same or different types of biocides.
  • Samples may be taken from the stream both before and after one or several point(s) of biocide addition.
  • FIG. 1 1 is a schematic picture of an exemplary control strategy (for an FB controller with a cascade loop) based on measurement s) according to the present invention in a suspension stream intended to undergo a one-step biocide treatment.
  • a measured data and/or calculated data and/or other process measurements from before or/and after the point of biocide addition may be used.
  • any known sensors or analyzers such as temperature sensors, pH sensors, ion selective electrodes, and anode stripping voltammetry for measuring the concentrations of heavy metals, dissolved oxygen sensor and any known surface fouling sensors or analyzers may be utilized in dosing control of biocides.
  • one or more of the above stated measurements in addition to one or more results of calculations according to the invention e.g. change in rH or relative change in rH, and relative dissolved oxygen consumption
  • a Linguistic Equation (LE) based soft sensors and online-measurements or calculations such as measurements of the temperature, the dissolved oxygen, or the rH, and calculations of the relative oxygen consumption, and the change or relative change in the rH value, are preferably utilized in the soft sensor calculation, and subsequently in the biocide dosage calculations.
  • suitable equipment we refer to the method and apparatus for automatic dose control of chemicals, described in WO 2005/022278, the contents of which are herewith incorporated by reference.
  • the operation of a device according to the invention is further illustrated in the following example:
  • Example in an exemplary process according to an embodiment of the invention is carried out using the configuration of Figure 12.
  • the device is controlled in accordance with the following programmed sequence, including sequential cycles of sampling, measuring and line washing.
  • the valves VI and V2 are opened, whereby the sample flows through the measuring unit.
  • the sampling cycle lasts for about 15 seconds, after which the valves VI and V2 are closed.
  • the measurement cycle begins upon closing of valves VI and V2, and lasts for about 2 h.
  • the temperature of the sample in the measurement vessel is maintained at a constant level using a Peltier element 16 for temperature control.
  • a set point of the controller is used a a value, which is provided by a PT-100 sensor 8 when 1 minute has passed after the start of the measuring cycle.
  • the first value of the concentration of the dissolved oxygen is read after 5 minutes from the start of the measurement cycle, and the second value is read at the end of the measuring cycle.
  • the difference between the first value and the second value are used for the calculation of the relative oxygen consumption.
  • a sampling line wash is started by opening valves VI and V6. Washing water is conducted to the sampling line 11 and finally to the main process line 13. Valve V2 is kept closed. The cycle lasts for 12 seconds. Once the line washing ends, the valves VI and V6 are closed. Outlet conduit 12 is open to the drain 18 whereby ambient, normal air pressure is present in the measurement vessel. Thus no pressure control is needed.
  • a new sampling cycle is started by opening valves VI and V2 whereby the measuring unit is discharged.

Landscapes

  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • General Health & Medical Sciences (AREA)
  • Biochemistry (AREA)
  • Analytical Chemistry (AREA)
  • Immunology (AREA)
  • Medicinal Chemistry (AREA)
  • Food Science & Technology (AREA)
  • General Physics & Mathematics (AREA)
  • Pathology (AREA)
  • Biomedical Technology (AREA)
  • Molecular Biology (AREA)
  • Organic Chemistry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Zoology (AREA)
  • Wood Science & Technology (AREA)
  • Emergency Medicine (AREA)
  • Biophysics (AREA)
  • Biotechnology (AREA)
  • Urology & Nephrology (AREA)
  • Hematology (AREA)
  • Proteomics, Peptides & Aminoacids (AREA)
  • Microbiology (AREA)
  • General Engineering & Computer Science (AREA)
  • Genetics & Genomics (AREA)
  • Toxicology (AREA)
  • Optics & Photonics (AREA)
  • Spectroscopy & Molecular Physics (AREA)
  • Sustainable Development (AREA)
  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Activated Sludge Processes (AREA)

Abstract

The present invention concerns a method of estimating and optionally controlling the microbiological state in a process stream of an industrial process by measuring the concentration of dissolved oxygen or the rH value, or both, in said stream, the method including continuous or periodic sampling and online measurement. The invention also concerns a device suitable for use in implementing said method.

Description

METHOD AND DEVICE FOR MONITORING AND CONTROLLING THE STATE OF A PROCESS STREAM Background of the Invention
Field of the Invention
The present invention concerns a method and device for monitoring and optionally controlling the microbiological state in process streams based on the measurement of variables, such as dissolved oxygen or rH or both, optionally assisted by soft sensors, based e.g. on Linquistic Equations (LE).
Description of the Related Art
A common problem in many industrial process systems, e.g. in paper and pulp processing systems, is microbial growth, if microbes are not controlled efficiently. Microbiological growth may cause several problems in the systems. The bacteria in a process stream may cause spoilage of the stream or bacteria may attach to system surfaces forming biofilm or slime. For example, biofilm masses that detach from system surfaces can be carried into the pulp waters and formed into the paper sheet thereby weakening the formed paper sheet quality, e.g. by causing it to tear or causing holes in the paper.
Industrial processes, such as the paper or board manufacturing process, often contain process stages where the process streams are kept in tanks for longer periods of time.
These process stages are ideal for the development of microbes, whereby there may be an increase in the microbial content of said streams. Other examples of locations ideal for microbiological growth in a process system are dead zones of process systems (e.g. poor mixing zones).
In the industrial process systems, e.g. in manufacturing of paper or board, microbe analyses are presently carried out in the laboratory due to the lack of fast online measuring methods and devices. The methods, e.g. plate count, are time-consuming and it can take up to 2-3 days to get the results of the analysis. Further, as there always exist a delay between the laboratory analysis results and the changes in the process conditions, the result may be an inadequate biocide dosage to the process stream and, thus, a poor paper quality as well as a poor cost-efficiency of the process. The same is true for other processes requiring biocides to maintain a low level of microbes in a process stream.
WO 2008/101089 describes a method of monitoring microbiological activity under aerobic conditions in process streams based on changes on dissolved oxygen concentrations measured using specified process steps. However, the measurement is claimed not to be suitable for process streams of low dissolved oxygen concentration. Further, the process is complex, requiring cleaning of the measuring probes between measurement points during measurement cycles.
Further, there is not available a method for reliably monitoring microbiological state under anaerobic conditions in process streams.
Thus, there is a need for simpler measurement methods to monitor the microbiological state of process streams, in particular on-line, and optionally to control microbiological state of process streams e.g. by controlling the effective amounts of biocide(s) to be added to the processes to maintain an acceptable microbiological state in said streams. In addition, there is a need to be able to monitor the microbiological state also at low dissolved oxygen concentrations in process streams, and in anaerobic conditions.
Summary of the Invention It is an aim of the present invention to eliminate at least a part of the problems relating to the known art and to provide a method and a device for the monitoring, optionally controlling of the microbiological state of a process stream.
A novel method and device for the analysis of process streams have now been developed. The invention is particularly suitable for use in monitoring, and optionally controlling the microbiological state of process streams, especially aqueous process streams. With microbiological state herein is referred to the activity of all such microorganisms that can influence the dissolved oxygen concentration and/or the rH value in a process stream, and optionally to aerobic or anaerobic conditions in a process stream. The idea is based on measuring parameters, such as the concentration of dissolved oxygen, and/or the rH, in a process stream. A sample is taken batch-wise from the process to a measuring unit and concentration of dissolved oxygen in the sample and/or rH of the sample is measured during a measuring cycle. The temperature is preferably also measured, as a more precise value for the concentration of dissolved oxygen can then be obtained.
Optionally, soft sensors based on any equation(s) and/or model(s), e.g. on Linquistic Equation (LE) models are preferably used to assist in the interpretation of the measurement data and/or calculated result data. In addition to the data according to the invention, other process data obtained by any known sensors or analyzers may be utilized to give an even more accurate perception of the microbiological state of the process streams for monitoring and optionally controlling the microbiological state of a process stream.
Thus, the present invention concerns a method and a device for monitoring and optionally controlling the microbiological state in a process stream by measuring the concentration of dissolved oxygen or the rH value, or both, in said stream.
More specifically, the method of the present invention is characterized by what is stated in Claim 1.
Further, the device of the present invention is characterized by what is stated in Claim 13 and the uses of the present invention are characterized by what is stated in Claims 19 and 20. This method and device make it possible to monitor the microbiological state of a process stream, in particular industrial stream, and to optionally control the microbiological state. The microbiological state can be controlled by controlling, preferably automatically, the amount of biocide(s) and/or location of the dosing of biocide(s) and/or selection of the type of biocide(s) to be added to the process stream, with a simple measurement method. The method allows also analysis of process streams with low concentration of dissolved oxygen. It also enables monitoring and optionally controlling the microbiological state of a process stream under anaerobic conditions. The method and the device may provide online data on the microbiological state of the analyzed process stream.
Next, the invention will be described more closely with reference to the attached drawings and a detailed description.
Brief Description of the Drawings
Figure 1 is a schematic picture of an arrangement to perform an embodiment of the method according to the invention.
Figure 2 is a graphical illustration of exemplary outputs of the online-measurement device of the present invention, showing the concentration of measured dissolved oxygen in the measurement unit and the temperature.
Figure 3 is a graphical illustration of the relative oxygen consumption and the amount of aerobic bacteria in an exemplary pulp suspension.
Figure 4 is a graphical illustration of the oxygen consumption (mg/1) and the relative oxygen consumption (%) of an exemplary pulp sample between ti and t2 in the measuring cycle. Figure 5a is a graphical illustration of the relative oxygen consumption and the oxygen consumption in an exemplary pulp sample at different moments of time during a measurement. Figure 5b shows the relative oxygen consumption and the amount of aerobic bacteria in the same exemplary pulp suspension. Figure 6 is a graphical illustration of the amount of microbes in an exemplary pulp suspension, as measured using a conventional laboratory analysis method and estimated using a soft sensor based on linquistic equations. Figure 7 is a graphical illustration of the effect of the pH on the redox value, as well as rH values corresponding to different process conditions, e.g. aerobic or anaerobic conditions.
Figure 8 is a graphical illustration of the amount of microbes at different rH values, Figure 8a showing a measured rH values over a period of time, where the number of aerobic bacteria increases as the rH value decreases, and Figure 8b showing the measured rH value versus amount (CFU) of anaerobic bacteria measured in the laboratory.
Figure 9 is a schematic picture of an exemplary control strategy based on measurement(s) according to the present invention in a suspension stream intended to undergo a two-step biocide treatment, with two separate addition points.
Figure 10 is a schematic picture of an exemplary control strategy (for a basic feedback FB controller) based on measurement s) according to the present invention in a suspension stream intended to undergo a one-step biocide treatment.
Figure 11 is a schematic picture of an exemplary control strategy (for an FB controller with a cascade loop) based on measurement s) according to the present invention in a suspension stream intended to undergo a one-step biocide treatment.
Detailed Description of Preferred Embodiments of the Invention
The present invention concerns a method and device for monitoring, and optionally controlling the microbiological state, of a process stream preferably of an industrial process by batchwise obtaining a sample of the suspension stream, measuring the concentration of dissolved oxygen or the rH value, or both, in said stream at least at two time points, calculating the relative oxygen consumption, the change of rH or the relative change of the rH, between two of said two or more time points, or calculating two or more of these, and determining microbiological state of the stream based on the measurements, and an device suitable for use in implementing said method. With the term "microbiological state" of a process stream, is referred to the activity of all such microorganisms that can influence the dissolved oxygen concentration and/or the rH value in a process stream, and optionally to aerobic or anaerobic conditions in a process stream.
Microbiological activity in process streams can be indirectly measured by monitoring the consumption of dissolved oxygen because dissolved oxygen consumption is directly related to aerobic metabolism of the cell. The higher the activity of the microorganisms, the higher the consumption of the dissolved oxygen is. Surprisingly, it was found that the relative dissolved oxygen consumption can be used to monitor microbiological state of a process stream. Relative dissolved oxygen consumption was found to be a very sensitive measurement for microbiological activity in accordance with the method of the invention in the aerobic conditions (i.e. when the concentration of dissolved oxygen is higher than 0 mg/1). Often the relative consumption of dissolved oxygen correlates also with the amount of the aerobic bacteria.
The rH value or especially the change or relative change thereof was found to describe microbiological activity under anaerobic and anoxic conditions. Under anaerobic and anoxic conditions microbes generate such products which tend to decrease rH value of the process stream. The rH value, change or relative change thereof often also correlates with the amount of anaerobic bacteria.
Further, rH value may correlate also in aerobic conditions with the amount of the aerobic bacteria in the suspension stream to be analyzed, especially when strongly oxidative chemicals are substantially absent in the sample. When the oxygen is being consumed by the microbes, the oxygen concentration is decreased and thereby the rH value decreases.
By measuring both concentration of dissolved oxygen and rH value in a process stream according to one embodiment of the invention, information on a wide area of process conditions can be obtained. The value(s) of dissolved oxygen concentration and rH measured at the beginning of a measuring cycle, describe whether the process conditions are anaerobic or aerobic. Thus, changes in a process stream from anaerobic to aerobic conditions, and vice versa, can be obtained. The initial values at the beginning of the measuring sequence may be used for selecting of the at least one measurement (dissolved oxygen or rH) used for determining the
microbiological state. Thus, combining information from the initial values of the measurement cycles or dissolved oxygen concentration and/or rH with one or more of change of rH, relative change of rH or relative change in oxygen consumption,
microbiological state of a process stream can be monitored, optionally controlled with the meathod of the invention both under aerobic and anaerobic conditions. This is especially preferred to be used in a process where the process conditions vary between anaerobic and aerobic process conditions.
An arrangement for performing a preferred embodiment of the method according to the invention is schematically illustrated in Figure 1.
The device according to the invention contains a measuring unit 10 with an inlet 23 and an outlet 24, means for measuring amount of dissolved oxygen 6 and/or means for measuring rH 7 within the measuring unit, with reference to Figure 1.
The device preferably contains an inlet conduit 11 for directing a sample to the measuring unit 10. The device may contain an outlet conduit 12 for directing the sample from the measuring unit. The inlet conduit 11 is in connection with a process line 13 whereby the inlet conduit allows taking a side-draw from the main process line 13. The said means 7 for measuring the rH value preferably includes: means 7a for measuring the redox potential, means 7b for measuring the pH value and preferably means 7c for calculating the rH value.
In an embodiment the device includes means 8 for measuring the temperature and optionally means 9 for measuring pressure.
Thus, the device of the present invention is suitable for monitoring, optionally controlling, the microbiological state in a process stream by measuring online the amount of dissolved oxygen or the rH, or both, in said stream.
In a preferred embodiment the device is in fluid connection with a process line 13 for a process stream. Process line 13 is equipped with a side draw 25 which may be the inlet conduit 1 1 for withdrawing a sample from said process stream, preferably a main process stream. Thereby the side draw 25 functions as a sampling point. The side draw 25 is in fluid connection with a measuring unit 10. The measuring unit is preferably a closed vessel with openings for entrance(s) of the sample flow, exit(s) of the sample, and any opening(s) for process equipment if needed, e.g. measuring probes or sensors, inlets for water or gas lines. Side draw 11 is preferably equipped with valve VI for sampling from process line 13. The vessel 10 is preferably lacking means for mixing the sample during the
measurement. The measuring unit 10 is intended for holding the sample during the measurement. The measuring unit may contain an inlet 14 with valve V4 for pressurized air to provide turbulence to the process stream between any chosen measurement cycle, thereby enabling cleaning of surfaces inside the measuring unit. The cleaning of the surfaces inside the vessel may additionally or alternatively be effected by providing water via inlet line 17 for washing water, including valve V5. In a preferred embodiment the device contains flow inlets only for the entrances of the sample flow to be measured.
Further, the device comprises means either for measuring the concentration of dissolved oxygen 6 or for measuring the redox 7a and pH 7b to determine rH of the sample within said measuring unit 10, or both 6, 7, as well as means 20 for processing the measurements and performing calculations based on the measured values (e.g. calculating relative dissolved oxygen consumption, rH, change or relative change of rH).
As stated above, the optional means 7 for measuring the rH of the sample preferably include means 7a for measuring the redox potential of the sample and means 7b for measuring the pH value of the sample, and preferably means 7c for calculating the rH value of the sample, and optionally means for measuring temperature.
The above mentioned means 6 for measuring the concentration of dissolved oxygen are preferably selected from (non-electrochemical) sensors not requiring the use of
membranes, as the sensors based on use of membranes become less sensitive with time (through ageing and fouling of the filters) and they require mixing of the sample or sufficient flow rate during the measurement and regular calibration. It is particularly preferred to use sensors utilizing optical measurement technology, e.g. luminescent dissolved oxygen (LDO) technology. The LDO sensors are available e.g. from Hach Company. As it is preferred to provide temperature and/or pressure control in methods for monitoring the microbiological state of a process stream, the device preferably comprises also means 8 for measuring the temperature of the sample within said measuring unit 10, and preferably also means 9 for measuring the pressure within said measuring unit 10. The means 8 for measuring the temperature are particularly preferred when applying the means 6 for measuring the concentration of dissolved oxygen. These means 6 may include separate means for measuring the temperature, such as a temperature sensor or a thermometer. The means 8 for measuring the temperature are particularly also preferred when applying the means 7 for measuring the rH.
The measuring unit may thus include means for measuring temperature of the sample within the vessel. Optionally, means 6 for measuring the concentration of dissolved oxygen and/or means for measuring rH of the sample may include additional means for measuring temperature.
It is also preferred to include into the device means 19 for controlling and monitoring the function of the device. This control and/or monitoring can take place on site or using a remote system. These means 19 are used, among others, for controlling the cycles and sequences of cycles, for temperature control, for controlling the calculations (e.g.
controlling the processing of the measurement) and for controlling the dosing of biocide(s). According to a preferred embodiment of the invention, the device further comprises means 21 for calculating the amount of biocide to be added into the process line 13, and means 22 for dosing said biocide into the process line 1. According to a particularly preferred embodiment of the present invention, the device includes a temperature controlled measurement vessel 10, inlet conduit 11 and washing line 15 with supplementary equipment, e.g. to regulate the flows in said lines (e.g valves VI, V2, V6), as well as a control unit 19. Since dissolution of oxygen in liquid e.g. water depends on the temperature, the temperature of the measurement reactor 10 is monitored and optionally controlled. The heating and/or the cooling of the measuring unit 16, that are required if the measurements are run at constant temperature, are realized using, e.g.
Peltier elements. The measurement vessel 10 is heated, e.g. by the electric resistance of the Peltier elements, and cooled by the cooling water circulation of the elements. If the temperature during the measurement is not constant or controlled, the effect thereof on the dissolution of oxygen can be compensated by calculations. Also an oxygen measurement sensor 6 and a temperature sensor 8, such as a PT-100 sensor, are installed in the vessel 10. The temperature sensor 8 is used to monitor the temperature of the vessel 10. In a preferred embodiment a sampling system comprises at least an inlet conduit 11, at least means (e.g. valve(s)) to regulate the sample flow between a process stream 13 and a measuring unit 10, and preferably an outlet conduit 12.
In a preferred embodiment a sampling line washing comprises at least a washing line 15 and at least means to regulate the washing water flow (e.g. valve V6 and VI) between a process stream 13 and a washing line 15.
Since pressure influences dissolution of oxygen in liquid e.g. water, in a preferred embodiment the pressure of the measuring unitlO is monitored and optionally controlled. Measurements of the dissolved oxygen and/or rH are preferably carried out in the normal air pressure. Normal air pressure can be obtained into the measurement vessel by opening valve V3 of the outlet conduit (12) before the measurement starts or by having the outlet conduit open to the normal pressure. In a preferred embodiment the V3 is not in the system.
In a preferred embodiment the means 20 for processing the measurements and performing calculations based on the measured values, means 19 for controlling and monitoring the function of the device and means for 21 for calculating the amount of biocide(s) are included in a same system, e.g. programmable logic and/or industrial PC.
A preferred device includes a measuring unit, online-sensors, sampling line washing, sampling systems, and programmable logic and/or industrial PC for processing the measurement results, controlling and monitoring the function of the device and for calculation the amount of biocides to be added into the process line.
The measured and/or calculated values according to the invention may be monitored locally or via a remote system, e.g. web-based. The method of the present invention for monitoring the microbiological state, in a process stream, includes the steps of
- providing a process stream originating from an industrial process;
- batch-wise conducting a sample of the process stream, preferably from a sampling point, to a measuring unit;
- measuring the concentration of dissolved oxygen or the rH, or both, in the sample within the measuring unit as a function of time, preferably at least at two time points;
- calculating relative oxygen consumption, or change of rH or relative change of the rH between two of said two or more time points, or calculating two or more of these; and
- determining, based on the rH value or on one or more of these calculated values, the microbiological state of the process stream. Another embodiment of a method of the present invention of monitoring the
microbiological state, in a process stream by measuring the concentration of dissolved oxygen or the rH, or both, in said stream, the method comprising
- providing a process stream originating from said process;
- batch-wise conducting a sample of the process stream, preferably from a sampling point, to a measuring unit;
- measuring, at two or more time points, the concentration of dissolved oxygen or the rH, or both, in the sample in the measuring unit;
- determining, based on one or more of calculated values or rH value, the
microbiological state of the process stream, wherein the calculated values include calculating relative oxygen consumption, or change of rH or relative change of the rH, or rate of the change of rH or consumption of dissolved oxygen between two of said two or more time points, or calculating two or more of these.
Optionally, the determined microbiological state in said stream is used to optimize the biocide program, e.g. to select a biocide or biocides and/or calculate an amount or dose of biocide(s) to be added into the process stream and/or to select the location of the addition point(s) of the biocide(s). It can also be used to identify the location and/or source of microbiological problems in a system of which the process stream is a part of, such as pulp, broke, water circulation and raw water, which can be present in, e.g. tanks, containers, pulpers and pipes.
Optionally, the determined microbiological state in said stream is used to control, preferably automatically, the microbiological state of the process stream by controlling the amount of biocide(s) added to the process stream, the selection of points of addition, or selection of the type of biocide(s) or any combination of the three. Preferably the controlling of microbiological state in said stream includes controlling the amount of biocide(s) added to the process stream, preferably by an automated control system.
In a preferred embodiment of the invention the method further comprises
controlling of microbiological state in said process stream by adding an amount of biocide(s) to the process stream, preferably by an automated control system.
By using the invention, it was found in a paper or board manufacturing process, that a stage that is ideal for microbial growth was the broke tank, where the broke can be stored for long periods of time, such as 2-1 Oh, or even days. The determined microbiological state may also be used to determine and control the desired delay time of process streams, such as the broke of a paper or board manufacturing process, in various tanks, since a shorter delay time might be required, for example, if there is a large increase in the microbe growth within said tank. According to a preferred embodiment of the invention, the device according to the invention is used in the implementation of this method.
The process stream to be analyzed may be any aqueous or non-aqueous liquid, optionally comprising solid matter. The solid matter can be in suspended and/or colloidal form. The process stream is particularly a process stream in a water circulation system of an industrial process, any aqueous suspension, such as paper or board pulp, wastewater, paper coating colour, activated sludge, inorganic sludge, or washing streams, such as the ones used in oil drilling or mining. The process stream may originate from an industrial water system or municipal water system. According to a preferred embodiment of the invention, the stream consists of paper or board pulp suspension including optional additives.
A process stream may be a flow or a stream in a process or stagnant, e.g. sample or content of a storage tank.
According to a preferred embodiment of the present invention, batch-wise sampling is used. A process stream is conducted to a measuring unit. When the measuring unit is filled with the process stream sample, the flow is interrupted to keep the sample in the measuring unit. The sampling is usually performed conducting a process stream through the measuring vessel for a period of time (sampling time) to obtain a representative sample. After sampling the flow is interrupted to keep the sample in the measuring unit. The sample is kept in the measuring unit for a period of time, i.e. a measuring cycle.
Measurements are performed at least at two time points during a measuring cycle. The time used for the measuring cycle is evaluated based on the general (average)
microbiological state of the stream to be analyzed. Preferably the measuring cycle varies between 1 minutes and 3 hours, more preferably between 15 minutes and 2 hours. An example of the output of measurements is shown in Figure 2. In this exemplary system the sampling time was 15 s and measuring cycle of dissolved oxygen was 2 h. In a preferred embodiment the measurements are performed during the whole measuring cycle, e.g. a measurement value is recorded 60 times per minute during the measuring cycle, e.g. during two hours.
The values measured (concentration of dissolved oxygen or a combination of pH and redox potential, or both of these) at least at the two time points are used to calculate the oxygen consumption (ADO), the relative oxygen consumption (ADO%), rH value (rH), the change of the rH value (ΔΓΗ) and/or the relative change of the rH value (ΔΓΗ%).
The oxygen consumption (mg/1) is calculated using equation (1):
C DO = 02 {t1) - 02 {t2) (X) and the relative oxygen consumption (%) is calculated using equation (2): ι)-02 (¾)
ADO% = 100% · 02
(2)
02 (ti) where 02(ti) is the first value of the concentration of dissolved oxygen. The first value is preferably measured at the beginning of the measuring cycle, e.g. within the first 15 minutes thereof. 02(t2) is the second value of the concentration of dissolved oxygen. The second value is preferably measured at the end of the measuring cycle, e.g. within the last 15 minutes of the measuring cycle.
The redox value is pH dependent. The rH value is calculated from the pH and redox potential using equation (3): rH = 2 * pH + 2 * Eh * F / (c.R.T) (3) wherein F = Faraday constant (9.64853399(24)x 104 C mof1, c = lnlO, T = temperature (K), Eh = redox potential measured with standard hydrogen electrode, and R = universal gas constant (8.314472(15) J K 1 mof1).
In the exemplary system of Figure 7, when T=20 °C (293 K).
rH = Eh / 0.029 + 2 * pH (4)
In this exemplary system, assuming that pH = 6.5 and Eh = -0.15 V: rH ~ 7.8
Further, as above for the oxygen consumption, the change of the rH value can be calculated using the following equation (5):
ArH = rH(tl) - rH(t2) (5) and the relative change of the rH value (%), using the following equation (6):
Figure imgf000017_0001
where rH(ti) is the first rH value. First rH value is preferably measured at the beginning of the measuring cycle, e.g. within the first 15 minutes thereof. rH(t2) is the second rH value and measured after the first value. The second rH value is preferably measured at the end of the measuring cycle, e.g. within the last 15 minutes thereof.
By recording more than two values the method and device of the present invention allow also online monitoring of the measured rH value and/or concentration of dissolved oxygen (as shown in Figure 2) during a measurement cycle. By using at least two, preferably more than two values of the measurements, thus allow a determination of, among others, the rate of oxygen consumption and/or rate of rH change during a measurement cycle. The rate of oxygen consumption and/or rate of rH change may also be used for selecting time period suitable for the measurement cycle and/or monitoring the microbiological state of the process stream.
The method is preferably carried out using a sequence of cycles, the cycles including at least one sampling cycle and at least one measuring cycle, preferably consisting of one sampling cycle and one measuring cycle. Thereby the method according to one
embodiment of the invention can be considered a continuous method. In one embodiment the next cycle follows the previous substantially immediately. The sampling cycle is usually shorter than the measuring cycle. Sampling time depends on the process, and may be e.g. between 60 seconds and 2 minutes. A suitable sampling time can be determined by a person skilled in the art. There can also be a time period between the cycles (after one sampling and measuring cycle has ended), e.g. if it is enough to receive monitoring data of the process stream only some times per day.
In a particular embodiment of the invention a process stream is conducted to a measuring unit without interrupting the process flow, and the rH value of the process flow is measured during the flow. The rH value is used to monitor, optionally control, the microbiological state of the process flow. It is preferred to utilize this embodiment especially for inorganic sludges, such as coating colors. Figure 8b show that rH value as such correlates with amount of anaerobic bacteria. rH may also correlate with amount of aerobic bacteria in some process streams, as shown in Figure 8a. However, in case of changes in the process flow other than microbiological, the rH value as such may not provide information on the microbiological state alone. To provide further control of the method, and an even more reliable result, the temperature of the sample and optionally the pressure in the measuring unit is measured. This is particularly useful when determining the microbiological state of the sample using the concentration of dissolved oxygen, as the dissolution of oxygen into liquid, e.g. water is temperature dependent and also pressure dependent. To take this dependency into account, the method can either be carried out at constant temperature, or the measured temperature can be included in the subsequent calculations to compensate for any changes in the temperature. The same applies for the pressure in the measuring unit during the
measurement. However, it is preferred to carry out both the measurement of the concentration of dissolved oxygen and the measurement of the rH at least at constant pressure, preferably at ambient pressure, which usually is normal air pressure, but most preferably also at constant temperature. In a still preferred embodiment of the invention the pressure and temperature in the measurement vessel during the measurement are kept constant. Thus, by determining the relative consumption of dissolved oxygen in a process stream, such as paper or board pulp, for example the pulped broke of a paper machine, conclusions can be made regarding the microbiological activity in the process stream, e.g. the pulp, and also amount of oxygen consuming microbes, particularly aerobic bacteria, in the process stream, e.g. the pulp. Similarly, by determining the rH, change of rH or relative change of rH in a process stream, such as, paper or board pulp suspension, conclusions can be made regarding the microbiological activity in the sample, and also amount of aerobic/anaerobic microbes in the sample.
Based on the conditions at the beginning of a measuring cycle it can be decided (preferably automatically) which at least one of the two measurements (the concentration of dissolved oxygen or the rH value) is used for determining the microbiological state of the process stream. In aerobic conditions (concentration of dissolved oxygen is higher than about 0 mg/1) it is preferred to measure concentration of the dissolved oxygen in the sample and use relative consumption of dissolved oxygen to determine the microbiological state of process stream. In anaerobic or anoxic conditions (concentration of dissolved oxygen is about 0 mg/1) it is preferred to measure rH value of the sample and use change or relative change of rH to determine the microbiological state of process stream. According to a preferred embodiment of the present invention, both concentration of the dissolved oxygen and the rH value are measured.
The initial value(s), preferably value(s) measured at the beginning of the measuring cycle, of dissolved oxygen concentration and rH describe whether the process conditions are anaerobic or aerobic and may be used for selecting of the at least one measurement (dissolved oxygen or rH) used for determining the microbiological state.
According to an embodiment of the invention, measurement of initial value(s) of the concentration of dissolved oxygen or the rH is carried out at the beginning of or before (e.g. during the sampling) the measurement cycle to determine whether the process stream conditions are aerobic or anaerobic. The results obtained in this initial measurement s) are preferably interpreted and used in selecting, preferably automatically, a suitable measurement parameter from the concentration of dissolved oxygen, the rH or their combination for a measurement cycle, preferably current or next, or any following measuring cycle, and optionally used to control the microbiological state of the process stream. Carrying out initial measurement of the concentration of dissolved oxygen or the rH at the beginning of the measurement cycle may be effected by analyzing one or several initial measurement values at the beginning of a measurement cycle, e.g. within the first 60 seconds of the measurement cycle. Thereby the suitable measurement parameter from the concentration of dissolved oxygen, the rH or their combination can be selected for the ongoing measurement cycle. The initial value can also be the value, first value, which is used in the calculations of change of rH, relative change of rH and/or relation oxygen consumption change.
In the present invention it is preferred that the measurement takes place online, as this makes it possible to react to the effects of temporary changes in the microbiological state of the analyzed stream. The concentration of dissolved oxygen in the process stream and/or the rH in the process stream can also be measured before taking the sample to or before it searches a measuring unit or during the process stream flows through the measuring unit. One or more of the said measurements obtained outside the measurement cycle can be used for monitoring, optionally controlling the microbiological state of the process stream as such or in combination with the calculated values obtained from the measurements outside the measuring cycle.
Often the relative dissolved oxygen consumption in a process stream correlates with the amount of aerobic bacteria in the process stream. Figure 3 shows relative oxygen consumption values determined with a method according to the invention vs. amount of aerobic bacteria on the sample, measured using the plate count method. When amount of microbes is high, the relative oxygen consumption during the measuring cycle is high. When the amount of microbes is low the relative oxygen consumption is small.
Oxygen can be consumed also by chemical oxidation reactions or oxygen can be released in chemical reactions (e.g. decomposition of H202). Chemical reactions have strongest effect immediately after chemical addition and usually require presence of strong oxidants. The effect of chemical reactions on the estimation of the microbiological state of a process stream can be taken into account or eliminated by selecting the measurement or sampling location. A person skilled in the art is capable of taking this into account.
Also the rH value of a process stream can be affected by changes in a process stream other than microbiological changes, such as changes in the bleaching of process flow or addition of strong oxidative chemicals. By measuring the change or relative change of the rH according to the invention the effect of the changes other than due to microbiological changes in the quality of a process stream can be eliminated. The effect of chemical reactions on the estimation of the microbiological state of a process stream can be taken into account or eliminated by selecting the measurement or sampling location. A person skilled in the art is capable of taking this into account.
Figure 4 shows examples of two measuring cycles where concentration of the dissolved oxygen (mg/1) in the sample was recorded. In the first example the first value at the beginning of measuring cycle is 6 mg/1 and the second value at the end of measuring cycle is 5 mg/1. Oxygen consumption during the measuring cycle is thus 1 mg/1 and relative oxygen consumption 17 %. In the second example the first value at the beginning of measuring cycle is 1 mg/1 and the second value in the end of measuring cycle is 0 mg/1. Oxygen consumption during the measuring cycle is 1 mg/1 and relatively oxygen consumption 100 %. In the first example the overall level of the concentration of the dissolved oxygen is high and the oxygen consumption as well as the relative oxygen consumption is quite low. This indicates that the microbiological activity is low and amount of bacteria is low whereby the microbiological state is good. In the second example the high relative oxygen consumption indicates poor microbiological state probably resulting from high activity of aerobic bacteria. In both examples the oxygen consumption is the same 1 mg/1. However, relative oxygen consumption in the two examples differs significantly.
Figure 5a is a graphical illustration of the relative oxygen consumption and the oxygen consumption in a pulp process stream as a function of time. Figure 5b shows the relative oxygen consumption and the amount of aerobic bacteria in the same exemplary process stream. The values of the oxygen consumption and relative oxygen consumption are obtained from sequential measurement cycles. In the results, Figure 5a shows a significant change in the relative oxygen consumption (%) as a function of time while the oxygen consumption (mg/1) remains nearly unchanged. Figure 5b shows that a significant change occurs also in the amount of aerobic bacteria. Thus, relative oxygen consumption may be used to give reliable information of the microbiological state of the process stream.
Thus, if monitoring only the oxygen consumption (mg/1), there is a risk that an alarming situation regarding the microbial state of a process stream is not noticed. Thereby, the amount of required biocides can be reliably controlled based on the relative oxygen consumption (%).
In addition the other parameters obtained by commercially available sensors or analyzers, such as temperature sensors, pH sensors, ion selective electrodes, for example for the analysis of chlorine and bromine, and anode stripping voltammetry for measuring the concentrations of heavy metals, and any known surface fouling sensors or analyzers may be utilized to give additional information of the microbiological quality of the process streams.
Soft sensors are preferably implemented in the method according to the invention. Soft sensors are additional estimation systems utilizing calculations to provide more detailed results of the microbiological state of a process. Soft sensors, e.g. based on Linquistic Equation (LE) models are preferably used to assist in the interpretation of measurement or calculated data, particularly in the method step of determining the microbiological state of the suspension, by providing equations used in calculations. The said data may be data obtained according to the method of the invention or other process measurements obtained by any known sensors or analyzers. For example the amount of microbes after chemical treatment can be predicted on the basis of the rH value and the amount of biocide residual using a soft sensor. The results of a soft sensor may be used as such or in combination with the method according to the invention to monitor, and optionally control the
microbiological state of a process stream. An exemplary result of a model based on soft sensors is shown in Fig. 6, as compared to the results of a laboratory analysis.
In a preferred embodiment of the invention the method further comprises controlling the microbiological state in said process stream by adding an effective amount of biocide(s) to the process stream, preferably by an automated control system.
In some preferred embodiments of the invention feedforward (FF), feedback (FB) control and/or FB controller with a cascade loop are used for controlling the microbiological state of the said process stream.
The measurements for the determination of the microbiological state according to the invention can be carried out on a sample of the process stream taken either before the stream reaches a point of biocide dosing in the process stream, or after this point. The output(s) of the method according to the invention can be used in dosing control of biocides (amount, type of, location). According to a preferred embodiment, the sample is taken before the stream reaches the biocide dosage point, and the results are used to control the subsequently required amount of biocide dose to be added to the process stream (i.e. feedforward (FF) control in Fig. 9). According to a preferred embodiment, the sample is taken after the biocide has been added, and the results are used to determine the success of the biocide treatment. Also in the latter case, the results may be used to control the required amount of biocide dose (i.e. feedback (FB) control, Fig. 10).
According to an alternative embodiment of the invention, samples are taken from the stream both before and after two points of biocide dosage as shown in Fig 9. Thus, there is provided a feedforward as well as a feedback control of the required amount of biocide addition. The said points of biocide dosages may dose the same or different types of biocides. Samples may be taken from the stream both before and after one or several point(s) of biocide addition.
According to an alternative embodiment of the invention, samples are taken from the stream both before and after a point of biocide dosage. Figure 1 1 is a schematic picture of an exemplary control strategy (for an FB controller with a cascade loop) based on measurement s) according to the present invention in a suspension stream intended to undergo a one-step biocide treatment. For controlling the set point value of the feedback controller a measured data and/or calculated data and/or other process measurements from before or/and after the point of biocide addition may be used.
Optionally other process measurements obtained by any known sensors or analyzers, such as temperature sensors, pH sensors, ion selective electrodes, and anode stripping voltammetry for measuring the concentrations of heavy metals, dissolved oxygen sensor and any known surface fouling sensors or analyzers may be utilized in dosing control of biocides. Optionally one or more of the above stated measurements in addition to one or more results of calculations according to the invention (e.g. change in rH or relative change in rH, and relative dissolved oxygen consumption) may be used in the soft sensor calculations, and subsequently in the biocide dosage calculations.
A Linguistic Equation (LE) based soft sensors and online-measurements or calculations, such as measurements of the temperature, the dissolved oxygen, or the rH, and calculations of the relative oxygen consumption, and the change or relative change in the rH value, are preferably utilized in the soft sensor calculation, and subsequently in the biocide dosage calculations. As regards to an example of suitable equipment we refer to the method and apparatus for automatic dose control of chemicals, described in WO 2005/022278, the contents of which are herewith incorporated by reference. The operation of a device according to the invention is further illustrated in the following example:
Example In an exemplary process according to an embodiment of the invention is carried out using the configuration of Figure 12. The device is controlled in accordance with the following programmed sequence, including sequential cycles of sampling, measuring and line washing. For the purpose of sampling, the valves VI and V2 are opened, whereby the sample flows through the measuring unit. The sampling cycle lasts for about 15 seconds, after which the valves VI and V2 are closed.
The measurement cycle begins upon closing of valves VI and V2, and lasts for about 2 h.
The temperature of the sample in the measurement vessel is maintained at a constant level using a Peltier element 16 for temperature control. As a set point of the controller is used a a value, which is provided by a PT-100 sensor 8 when 1 minute has passed after the start of the measuring cycle.
In this Example, the first value of the concentration of the dissolved oxygen is read after 5 minutes from the start of the measurement cycle, and the second value is read at the end of the measuring cycle. The difference between the first value and the second value are used for the calculation of the relative oxygen consumption.
Simultaneously with the measurement cycle, a sampling line wash is started by opening valves VI and V6. Washing water is conducted to the sampling line 11 and finally to the main process line 13. Valve V2 is kept closed. The cycle lasts for 12 seconds. Once the line washing ends, the valves VI and V6 are closed. Outlet conduit 12 is open to the drain 18 whereby ambient, normal air pressure is present in the measurement vessel. Thus no pressure control is needed. When the measurement cycle is completed, a new sampling cycle is started by opening valves VI and V2 whereby the measuring unit is discharged.
The results obtained using a similar programmed sequence, with the same time period used for the measurement cycle, is shown in Figure 2.

Claims

Claims:
1. A method of monitoring the microbiological state, in a process stream by measuring the concentration of dissolved oxygen or the rH, or both, in said stream, the method comprising
- providing a process stream originating from said process;
- batch-wise conducting a sample of the process stream to a measuring unit;
- measuring, at two or more time points, the concentration of dissolved oxygen or the rH, or both, in the sample in the measuring unit;
- calculating relative oxygen consumption, or change or relative change of the rH between two of said two or more time points , or calculating two or more of these, and
- determining, based on one or more of the calculated values or based on the rH
value, the microbiological state of the process stream.
2. The method according to claim 1, wherein the process stream is an industrial stream, preferably a stream of paper or board pulp suspension.
3. The method according to claim 1 or 2, wherein the temperature of the sample and the pressure in the measuring unit are measured and optionally used in the calculations.
4. The method according to any of claims 1 to 3, wherein the measurement of the concentration of dissolved oxygen or the rH, or both, is carried out at constant pressure, or at constant temperature, or with both the temperature and the pressure being constant.
5. The method according to any of claims 1 to 4, wherein the rH is determined by measuring the pH value and the redox potential of the sample and calculating the rH value.
6. The method according to any of claims 1 to 5, wherein the step of determining the microbiological state includes calculations using the following equation for the relative oxygen consumption:
ADO% = 100% - °2 (tl)"°2 (t2) (2) and optionally the following equations for the rH values: rH = 2 * pH + 2 * Eh * F / (c.R.T)(3),
ArH = rH(tl) - rH(t2) (5)
and
Figure imgf000027_0001
7. The method according to any of claims 1 to 6, wherein an initial value of the
concentration of dissolved oxygen and/or the rH is carried out at the beginning of or before the measurement cycle to determine whether the process stream conditions are aerobic or anaerobic.
8. The method according to claim 7, wherein the results obtained in the initial
measurement are used in selecting a suitable measurement parameter from the
concentration of dissolved oxygen, the rH or their combination, and optionally at least a part of the results thus obtained are used to monitoring and/or control the microbiological state of the process stream.
9. The method according to any of claims 1 to 8, wherein soft sensors, particularly based on Linquistic Equation (LE) models, are used to assist in the interpretation of the measurement data and/or calculated data, and optionally any other process data, to determine the microbiological state of the process stream.
10. The method according to any of claims 1 to 9, further comprising controlling, preferably automatically, the microbiological state of the process stream by controlling the amount of biocide(s) added to the process stream, the selection of points of addition, or selection of the type of biocide(s) or any combination of the three.
11. The method according to any of claims 1 to 10, further comprising controlling of microbiological state in said stream by adding an amount of biocide(s) to the process stream, preferably by an automated control system.
12. The method according any of claims 1 to 11, which further includes identification of process streams to be monitored, preferably selected from pulp, broke, water circulation and raw water, and/or locations of these process streams to be monitored, preferably selected from tanks, containers, pulpers and pipes.
13. An online device for monitoring the microbiological state in a process stream of an industrial process by measuring the concentration of dissolved oxygen or the rH, or both, in said stream, the device comprising
- a measuring unit (10) with an inlet (23) and an outlet (24) intended for holding the sample to be measured; and
- means for measuring the concentration of dissolved oxygen (6) or means for
measuring the rH (7) of the sample within said measuring unit (10), or both means.
14. The device according to Claim 13, further comprising an inlet conduit (11) for directing a sample to the measuring unit (10) and an outlet conduit (12) for directing the sample away from the measuring unit (10), the inlet conduit (11) being in connection with a process line (13), whereby the inlet conduit allows taking a side-draw from the main process line (13).
15. The device according to claim 13 or 14, wherein the means (7) for measuring the rH of the sample include means for measuring the redox potential (7a), means for measuring the pH value (7b), and means for calculating the rH (7c) of the sample based on the pH value and the redox potential.
16. The device according to any of claims 13 to 15, further comprising means for measuring the temperature (8) and means for measuring the pressure (9).
17. The device according to any of claims 13 to 16, further comprising means for controlling and monitoring the function of the device (19).
18. The device according to any of claims 13 to 17, further comprising means for calculating the amount of biocide (21) to be added into the process line (13) and means for dosing said biocide (22) into the process line (13).
19. Use of the method of any of claims 1 to 12 for determining the microbiological state in the pulp of a paper or board manufacturing process.
20. Use of the device according to any of claims 13 to 18 in the process of any of claims 1
PCT/FI2012/051190 2011-12-02 2012-11-30 Method and device for monitoring and controlling the state of a process stream WO2013079801A1 (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
US14/362,135 US9970919B2 (en) 2011-12-02 2012-11-30 Method and device for monitoring and controlling the state of a process stream
CA2857383A CA2857383C (en) 2011-12-02 2012-11-30 Method and device for monitoring and controlling the state of a process stream
CN201280059316.7A CN103959059B (en) 2011-12-02 2012-11-30 Method and apparatus for the state that process streams are monitored and controlled
EP12816314.4A EP2786136B1 (en) 2011-12-02 2012-11-30 Method and device for monitoring and controlling the state of a process stream
ES12816314T ES2741651T3 (en) 2011-12-02 2012-11-30 Method and device to monitor and control the status of a process stream
BR112014013342-5A BR112014013342B1 (en) 2011-12-02 2012-11-30 method and device for monitoring and controlling the status of a process flow

Applications Claiming Priority (4)

Application Number Priority Date Filing Date Title
US201161566023P 2011-12-02 2011-12-02
US61/566,023 2011-12-02
FI20116227A FI126240B (en) 2011-12-02 2011-12-02 Method and device for monitoring and controlling the state of a process
FI20116227 2011-12-02

Publications (1)

Publication Number Publication Date
WO2013079801A1 true WO2013079801A1 (en) 2013-06-06

Family

ID=48534737

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/FI2012/051190 WO2013079801A1 (en) 2011-12-02 2012-11-30 Method and device for monitoring and controlling the state of a process stream

Country Status (8)

Country Link
US (1) US9970919B2 (en)
EP (1) EP2786136B1 (en)
CN (1) CN103959059B (en)
BR (1) BR112014013342B1 (en)
CA (1) CA2857383C (en)
ES (1) ES2741651T3 (en)
FI (1) FI126240B (en)
WO (1) WO2013079801A1 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020109660A1 (en) * 2018-11-27 2020-06-04 Kemira Oyj Method for estimating the vapor phase corrosion load
US11598051B2 (en) 2017-06-21 2023-03-07 Kemira Oyj Method for manufacturing a fibrous web
US11859347B2 (en) 2017-12-08 2024-01-02 Kemira Oyj Method for predicting or controlling microbial status of a paper or board making process
GB2622005A (en) * 2022-08-30 2024-03-06 Kemira Oyj Water treatment

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FI20136173L (en) * 2013-11-24 2015-05-25 Kemira Oyj Optical determination of the anionic charge in a flow
US9772303B2 (en) * 2015-01-12 2017-09-26 Ecolab Usa Inc. Apparatus for, system for and methods of maintaining sensor accuracy
US9810676B2 (en) * 2015-01-12 2017-11-07 Ecolab Usa Inc. Apparatus for, system for and methods of maintaining sensor accuracy
EP3385366A1 (en) * 2017-04-04 2018-10-10 Siemens Aktiengesellschaft Method for controlling a biotechnological process
CN109884263B (en) * 2019-03-28 2023-12-15 江苏核电有限公司 Dissolved oxygen sensor test device and test method thereof
CN114945815A (en) 2019-10-24 2022-08-26 埃科莱布美国股份有限公司 System and method for online deposit detection in process fluids
US20240053305A1 (en) * 2022-08-04 2024-02-15 Saudi Arabian Oil Company Rapid method for different types of biocide residual with analysis procedure
WO2024047067A1 (en) * 2022-08-30 2024-03-07 Kemira Oyj Water treatment

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3731522A (en) * 1970-09-30 1973-05-08 Robertshaw Controls Co Method and apparatus for determining oxygen consumption rate in sewage
US4073692A (en) * 1975-04-21 1978-02-14 Ciaccio Leonard L Method and apparatus for automated measurement of energy oxygen
GB2184110A (en) * 1985-12-11 1987-06-17 Boc Group Plc Treatment of aqueous material
WO2005022278A1 (en) 2003-08-29 2005-03-10 Kemira Oyj Method and device arrangement for automatic dose control of chemicals
WO2008101089A2 (en) 2007-02-16 2008-08-21 Nalco Company A method of monitoring microbiological activity in process streams
DE102009007851A1 (en) * 2009-02-06 2010-08-12 Kurt-Schwabe-Institut für Mess- und Sensortechnik e.V. Meinsberg Sensor for detecting relative hydrogen value for e.g. food industry, has pH electrode, half cell and electrochemical reference electrode that are formed on planar substrate using planar technology

Family Cites Families (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
MY129784A (en) 1996-01-22 2007-04-30 Biochem Technology Inc Method for monitoring biological activity in fluids
US8173438B1 (en) 1996-10-08 2012-05-08 Photonic Biosystems, Inc. Microbiological assessment method and device utilizing oxygen gradient sensing
FR2786782B1 (en) 1998-12-04 2001-02-23 Biomerieux Sa METHOD FOR DETECTION OF MICROORGANISMS AND MEDIUM FOR USE IN SUCH A METHOD
DE20001351U1 (en) 2000-01-27 2000-05-11 NAN Gesellschaft für Meßtechnik und Pilotanlagen mbH, 47877 Willich Biomeasuring cell
NL1026287C2 (en) 2004-05-28 2005-11-30 Vitens Fryslsn Measuring microbiological activity of aqueous solutions, used for monitoring drinking water quality, by measuring reduction in oxygen concentration over time
DE102004048316A1 (en) 2004-10-05 2006-04-13 Schellbach, Winfried On-line qualitative evaluation of germ level in circulating water of open refrigeration and air conditioning plants, by determining dynamic oxygen consumption in micro-throughflow measuring chamber
JPWO2006054738A1 (en) * 2004-11-22 2008-06-05 ノバルティスアニマルヘルス株式会社 Process for activated sludge treatment of milbemycin compounds and avermectin compounds
JP4764763B2 (en) 2006-04-20 2011-09-07 株式会社日新化学研究所 Viable count method, viable count device, slime monitoring method and slime control agent addition system
US7949432B2 (en) 2007-02-16 2011-05-24 Nalco Company Method of monitoring surface associated microbiological activity in process streams
US9453798B2 (en) * 2010-12-01 2016-09-27 Nalco Company Method for determination of system parameters for reducing crude unit corrosion
US9409110B2 (en) * 2011-07-14 2016-08-09 Nalco Company Method of maintaining water quality in a process stream

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3731522A (en) * 1970-09-30 1973-05-08 Robertshaw Controls Co Method and apparatus for determining oxygen consumption rate in sewage
US4073692A (en) * 1975-04-21 1978-02-14 Ciaccio Leonard L Method and apparatus for automated measurement of energy oxygen
GB2184110A (en) * 1985-12-11 1987-06-17 Boc Group Plc Treatment of aqueous material
WO2005022278A1 (en) 2003-08-29 2005-03-10 Kemira Oyj Method and device arrangement for automatic dose control of chemicals
WO2008101089A2 (en) 2007-02-16 2008-08-21 Nalco Company A method of monitoring microbiological activity in process streams
DE102009007851A1 (en) * 2009-02-06 2010-08-12 Kurt-Schwabe-Institut für Mess- und Sensortechnik e.V. Meinsberg Sensor for detecting relative hydrogen value for e.g. food industry, has pH electrode, half cell and electrochemical reference electrode that are formed on planar substrate using planar technology

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
BACHMANN ET AL: "Investigating and modelling the development of septic sewage in filled sewers under static conditions: A lab-scale feasibility study", SCIENCE OF THE TOTAL ENVIRONMENT, ELSEVIER, AMSTERDAM, NL, vol. 388, no. 1-3, 17 October 2007 (2007-10-17), pages 194 - 205, XP022300460, ISSN: 0048-9697, DOI: 10.1016/J.SCITOTENV.2007.08.004 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US11598051B2 (en) 2017-06-21 2023-03-07 Kemira Oyj Method for manufacturing a fibrous web
US11859347B2 (en) 2017-12-08 2024-01-02 Kemira Oyj Method for predicting or controlling microbial status of a paper or board making process
WO2020109660A1 (en) * 2018-11-27 2020-06-04 Kemira Oyj Method for estimating the vapor phase corrosion load
US12072279B2 (en) 2018-11-27 2024-08-27 Kemira Oyj Method for estimating the vapor phase corrosion load
GB2622005A (en) * 2022-08-30 2024-03-06 Kemira Oyj Water treatment

Also Published As

Publication number Publication date
CN103959059B (en) 2018-04-27
CN103959059A (en) 2014-07-30
EP2786136A1 (en) 2014-10-08
EP2786136B1 (en) 2019-05-15
BR112014013342A2 (en) 2017-06-13
BR112014013342B1 (en) 2021-03-16
US20140343872A1 (en) 2014-11-20
CA2857383A1 (en) 2013-06-06
CA2857383C (en) 2021-08-31
US9970919B2 (en) 2018-05-15
ES2741651T3 (en) 2020-02-11
FI126240B (en) 2016-08-31
FI20116227A (en) 2013-06-03

Similar Documents

Publication Publication Date Title
EP2786136B1 (en) Method and device for monitoring and controlling the state of a process stream
KR101387036B1 (en) A method of monitoring microbiological activity in process streams
JP2771611B2 (en) Cooling tower water continuous on-stream monitoring device
US6998057B2 (en) Method for monitoring and controlling chlorine levels in an aqueous medium
EP4049006B1 (en) System and method of inline deposit detection in process fluid
JP2011169859A (en) Method and device for automatically managing chlorine concentration
JP2009095742A (en) Method for preventing slime and system for adding halogen-based disinfectant
US6555379B1 (en) Device for monitoring a processing liquid
JP6191404B2 (en) Sludge activity measuring apparatus and sludge activity measuring method
ITMI961330A1 (en) SYSTEM FOR MONITORING BIOCIDAL TREATMENTS
JP7284634B2 (en) Cooling tower water quality control device and its water quality control method
JP2001318057A (en) Residual chlorine measuring method and its device
JP4764763B2 (en) Viable count method, viable count device, slime monitoring method and slime control agent addition system
KR20110072628A (en) Automatic measuring apparatus and method of concentration mixed acid
EP3643684A1 (en) System and procedure for the disinfection and preservation of water in circuits with water accumulation by means of applying combined electroporation and oxidation
JPH04354898A (en) Method for measuring concentration of component in neutral-salt electrolytic bath for descaling stainless steel

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 12816314

Country of ref document: EP

Kind code of ref document: A1

WWE Wipo information: entry into national phase

Ref document number: 2012816314

Country of ref document: EP

ENP Entry into the national phase

Ref document number: 2857383

Country of ref document: CA

NENP Non-entry into the national phase

Ref country code: DE

WWE Wipo information: entry into national phase

Ref document number: 14362135

Country of ref document: US

REG Reference to national code

Ref country code: BR

Ref legal event code: B01A

Ref document number: 112014013342

Country of ref document: BR

ENP Entry into the national phase

Ref document number: 112014013342

Country of ref document: BR

Kind code of ref document: A2

Effective date: 20140602