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US20100236732A1 - Use of fluorescence to monitor hydrophobic contaminants in a papermaking process - Google Patents

Use of fluorescence to monitor hydrophobic contaminants in a papermaking process Download PDF

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Publication number
US20100236732A1
US20100236732A1 US12/405,797 US40579709A US2010236732A1 US 20100236732 A1 US20100236732 A1 US 20100236732A1 US 40579709 A US40579709 A US 40579709A US 2010236732 A1 US2010236732 A1 US 2010236732A1
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Prior art keywords
fluid
contaminants
dye
papermaking process
hydrophobic
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Abandoned
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US12/405,797
Inventor
Alessandra Gerli
Laura M. Sherman
Michael J. Murcia
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Ecolab USA Inc
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Individual
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Priority to US12/405,797 priority Critical patent/US20100236732A1/en
Assigned to BANK OF AMERICA, N.A., AS COLLATERAL AGENT reassignment BANK OF AMERICA, N.A., AS COLLATERAL AGENT SECURITY AGREEMENT Assignors: CALGON LLC, NALCO COMPANY, NALCO CROSSBOW WATER LLC, NALCO ONE SOURCE LLC
Assigned to NALCO COMPANY reassignment NALCO COMPANY ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: MURCIA, MICHAEL J., SHERMAN, LAURA M., GERLI, ALESSANDRA
Priority to TW099105147A priority patent/TW201035538A/en
Priority to ARP100100747A priority patent/AR075742A1/en
Priority to PCT/US2010/027391 priority patent/WO2010107731A1/en
Publication of US20100236732A1 publication Critical patent/US20100236732A1/en
Assigned to NALCO COMPANY reassignment NALCO COMPANY RELEASE BY SECURED PARTY (SEE DOCUMENT FOR DETAILS). Assignors: BANK OF AMERICA, N.A.
Assigned to NALCO COMPANY reassignment NALCO COMPANY RELEASE BY SECURED PARTY (SEE DOCUMENT FOR DETAILS). Assignors: BANK OF AMERICA, N.A.
Assigned to ECOLAB USA INC. reassignment ECOLAB USA INC. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: CALGON CORPORATION, CALGON LLC, NALCO COMPANY LLC, ONDEO NALCO ENERGY SERVICES, L.P.
Assigned to NALCO COMPANY LLC reassignment NALCO COMPANY LLC CHANGE OF NAME (SEE DOCUMENT FOR DETAILS). Assignors: NALCO COMPANY
Assigned to ECOLAB USA INC. reassignment ECOLAB USA INC. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: NALCO COMPANY
Abandoned legal-status Critical Current

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    • 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
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/62Systems in which the material investigated is excited whereby it emits light or causes a change in wavelength of the incident light
    • G01N21/63Systems in which the material investigated is excited whereby it emits light or causes a change in wavelength of the incident light optically excited
    • G01N21/64Fluorescence; Phosphorescence
    • G01N21/6428Measuring fluorescence of fluorescent products of reactions or of fluorochrome labelled reactive substances, e.g. measuring quenching effects, using measuring "optrodes"
    • G01N21/643Measuring fluorescence of fluorescent products of reactions or of fluorochrome labelled reactive substances, e.g. measuring quenching effects, using measuring "optrodes" non-biological material
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/62Systems in which the material investigated is excited whereby it emits light or causes a change in wavelength of the incident light
    • G01N21/63Systems in which the material investigated is excited whereby it emits light or causes a change in wavelength of the incident light optically excited
    • G01N21/64Fluorescence; Phosphorescence
    • G01N21/6428Measuring fluorescence of fluorescent products of reactions or of fluorochrome labelled reactive substances, e.g. measuring quenching effects, using measuring "optrodes"
    • G01N2021/6439Measuring fluorescence of fluorescent products of reactions or of fluorochrome labelled reactive substances, e.g. measuring quenching effects, using measuring "optrodes" with indicators, stains, dyes, tags, labels, marks

Definitions

  • This invention pertains to the measurement and control of hydrophobic contaminants.
  • Hydrophobic/organic contaminants such as natural pitch, stickies, tackies and white pitch are major obstacles in paper manufacturing because these materials when liberated during a papermaking process can become both undesirable components of papermaking furnishes and troublesome to the mill equipment by preventing proper operation of mechanical parts when these materials deposit.
  • the present invention provides for a method of monitoring one or more types of hydrophobic contaminants in a papermaking process comprising: (a) obtaining a bulk sample of fluid from said papermaking process; (b) selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; (c) adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; (d) measuring the fluorescence of the dye in said fluid; (e) correlating the fluorescence of the dye with the concentration of said contaminants; and (f) optionally controlling the amount of one or more chemicals that reduce or inactivate said contaminants which are added to said papermaking process.
  • the present invention also provides for a method for measuring the effectiveness of one or more chemicals that decrease the amount of one or more hydrophobic contaminants in a papermaking process: (a) monitoring one or more types of contaminants in a papermaking process comprising: obtaining a bulk sample of fluid from said papermaking process; selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; measuring the fluorescence of the dye in said fluid; and correlating the fluorescence of the dye with the concentration of said contaminants; (b) adding one or more chemicals to said papermaking process that decrease the amount of said hydrophobic contaminants; and (c) re-measuring the amount of contaminants in said papermaking process by performing step (a) at least one more time; and (d) optionally controlling the amount of said chemicals that are added to said papermaking process.
  • the present invention also provides for a method of monitoring one or more types of hydrophobic contaminants in a papermaking process consisting essentially of: (a) obtaining a bulk sample of fluid from said papermaking process; (b) selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; (c) adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; (d) measuring the fluorescence of the dye in said fluid; (e) correlating the fluorescence of the dye with the concentration of said contaminants; and (f) optionally controlling the amount of one or more chemicals that reduce or inactivate said contaminants which are added to said papermaking process.
  • Papermaking process means a method of making any kind of paper products (e.g. paper, tissue, board, etc.) from pulp comprising forming an aqueous cellulosic papermaking furnish, draining the furnish to form a sheet and drying the sheet The steps of forming the papermaking furnish, draining and drying may be carried out in any manner generally known to those skilled in the art.
  • the papermaking process may include a pulping stage, e.g. making pulp from woody raw material and bleaching stage, e.g. chemical treatment of the pulp for brightness improvement. Furnishes can contain fillers and/or other contaminants.
  • Bulk sample means a sample whose constituents have not been specifically separated, except bulk sample may include, a separation based upon size. For example, bulk sample does not include separating e.g. a resin particle from a suspension.
  • Fluid includes an aqueous papermaking suspension from a papermaking process, e.g. a fluid containing fibers in a pulping stage, a thin stock, a thick stock, aqueous suspensions drawn from the papermaking process, e.g. various locations from a papermaking machine or pulping process, aqueous fluid in a uhl box, press dewatering section, and/or any part of the papermaking process that one of ordinary skill in the art can think of where one would need to monitor hydrophobic contaminants.
  • aqueous papermaking suspension from a papermaking process e.g. a fluid containing fibers in a pulping stage, a thin stock, a thick stock, aqueous suspensions drawn from the papermaking process, e.g. various locations from a papermaking machine or pulping process, aqueous fluid in a uhl box, press dewatering section, and/or any part of the papermaking process that one of ordinary skill in the art can think of where one would need to monitor hydrophobic
  • the present invention provides for a method of monitoring one or more types of hydrophobic contaminants in a papermaking process via the use of fluorescence.
  • the dyes, which are added to the sample must be able to stain or interact with the hydrophobic contaminants, e.g. pitch particles.
  • the turbidity of the fluid is also measured. In a further embodiment, the turbidity of said fluid is measured before and after the addition of said chemicals.
  • the fluid is filtered or diluted or a combination thereof prior to said addition of said dye or said fluorescent measurement of said dye, wherein said filtering or dilution of said fluid permits said fluid to be fluorometrically monitored.
  • the sample is taken from a dilute sample point off a papermaking process, e.g. a paper machine.
  • the sample point is the white water of a papermaking process. The reasoning postulated for this collection/sample point is that there is no long fiber present/substantially any fiber present, and filtration may not be necessary.
  • one or more samples undergo a sieving/separation step to separate the long fiber from the suspended contaminants in a sample solution.
  • the degree of dilution that the filtrate/aqueous fraction undergoes from the separation process relies on two main factors, both relating to turbidity. If the filtrate/aqueous fraction is too turbid for the turbidimeter, dilution is required to bring the turbidity into a measurable range for the meter. This is the case unless you want a less accurate and “quick and dirty” test, which is one embodiment of the claimed invention.
  • turbidity is above 2000 NTU (nephelometric turbidity units)
  • a sample from a papermaking process is diluted/further separated prior to the addition of a dye and fluorescent measurement.
  • the value of 2000 NTU may be instrument or measurement technique dependent.
  • the fluid is an aqueous filtrate of a pulp slurry.
  • the dye does not include N-(n-butyl)4-(n-butylamino)-naphthalimide.
  • the fluid is obtained from a wet end of said papermaking process.
  • the dye added to a sample must have a sufficient amount of time for said dye to interact with said contaminants in said fluid prior to its fluorescent measurement.
  • One of ordinary skill in the art could determine a sufficient amount of time for said interaction without undue experimentation.
  • the dye is mixed with a solvent prior to its addition to said fluid.
  • a solvent prior to its addition to said fluid.
  • the contaminants are selected from the group consisting of: pitch, fiber, filler, fines, coated broke, mill broke, recycle, groundwood, thermal mechanical pulp, chemi-thermal mechanical pulp, chemical pulp, deinked pulp, ink, adhesives, stickies, tackies, waxes, binders and dissolved and/or colloidal substances, and a combination thereof.
  • the method is an on-line method and/or batch sample method.
  • the fluorometric measurement is performed at a pre-set basis, intermittent basis, and/or continuous basis.
  • a flow cell can be utilized as a means for measuring the fluorescence of said hydrophobic contaminants.
  • a process for measurement comprises: the addition of one or more fluorescent tracers to a sample obtained from a papermaking process prior to its fluorescent measurement in said flow cell.
  • the fluorometric measurement is performed with a handheld fluorometer.
  • a fluorescent measurement may be carried out with other types of fluorometers.
  • the present invention also provides for a method of measuring the effectiveness of one or more chemicals that decrease the amount of one or more hydrophobic contaminants in a papermaking process.
  • the information on the amount of hydrophobic contaminants in a fluid can be utilized to form a control loop for the addition of one or more chemicals, which can be used to control the amount of hydrophobic contaminants.
  • the methodology for monitoring the hydrophobic contaminants can be measured by the above-stated fluorescence methodology and its various embodiments.
  • a determination of the amount of fluorescence is measured by the above-mentioned protocol, then subsequent to this step, an addition of one or more chemicals to the papermaking process to treat the hydrophobic contaminants, e.g. increase/decrease in the same chemistry for hydrophobic contaminant inhibition or change in the chemistry treatment program for hydrophobic contaminant inhibition, and then subsequent to the treatment step, a re-measurement of the amount of contaminants in said papermaking process by the above-mentioned protocol.
  • the chemicals are at least one of the following: a fixative; a detackifier; a dispersant; a surfactant; and a retention aid.

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  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Immunology (AREA)
  • Physics & Mathematics (AREA)
  • General Physics & Mathematics (AREA)
  • Biochemistry (AREA)
  • Pathology (AREA)
  • General Health & Medical Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Molecular Biology (AREA)
  • Nuclear Medicine, Radiotherapy & Molecular Imaging (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Optics & Photonics (AREA)
  • Engineering & Computer Science (AREA)
  • Food Science & Technology (AREA)
  • Medicinal Chemistry (AREA)
  • Investigating, Analyzing Materials By Fluorescence Or Luminescence (AREA)
  • Paper (AREA)

Abstract

A method of monitoring and controlling one or more types of hydrophobic contaminants in a papermaking process is disclosed. The methodology utilizes the measurement of dyes, which are capable of fluorescing and interacting with the hydrophobic contaminants.

Description

    FIELD OF THE INVENTION
  • This invention pertains to the measurement and control of hydrophobic contaminants.
  • BACKGROUND OF THE INVENTION
  • Hydrophobic/organic contaminants, such as natural pitch, stickies, tackies and white pitch are major obstacles in paper manufacturing because these materials when liberated during a papermaking process can become both undesirable components of papermaking furnishes and troublesome to the mill equipment by preventing proper operation of mechanical parts when these materials deposit.
  • Increased use of secondary fiber, coated broke and mechanical pulp in the papermaking process contributes to the accumulation of organic contaminants. These contaminants can form deposits that affect machine runability and final product quality. Control of the contaminants is typically managed through chemical fixation, and its effectiveness is therefore dependent on the ability to determine the proper program and application. Historically, a common method used to assess program performance has been filtrate turbidity reduction. This method, however, is not entirely adequate because it often yields an incomplete picture of the furnish demands from hydrophobic particles. More recently, flow cytometry has been used in the industry for monitoring hydrophobic contaminants. Disadvantages of this method are that it is both labor and capital intensive.
  • A rapid and accurate method of measuring organic contaminants is therefore desired. Chemical control programs are often used to passivate or remove deposit-forming contaminants. For that reason, a method of screening the efficacy of chemical treatments that reduce the overall content of hydrophobic contaminants in a papermaking process is also desired.
  • SUMMARY OF THE INVENTION
  • The present invention provides for a method of monitoring one or more types of hydrophobic contaminants in a papermaking process comprising: (a) obtaining a bulk sample of fluid from said papermaking process; (b) selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; (c) adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; (d) measuring the fluorescence of the dye in said fluid; (e) correlating the fluorescence of the dye with the concentration of said contaminants; and (f) optionally controlling the amount of one or more chemicals that reduce or inactivate said contaminants which are added to said papermaking process.
  • The present invention also provides for a method for measuring the effectiveness of one or more chemicals that decrease the amount of one or more hydrophobic contaminants in a papermaking process: (a) monitoring one or more types of contaminants in a papermaking process comprising: obtaining a bulk sample of fluid from said papermaking process; selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; measuring the fluorescence of the dye in said fluid; and correlating the fluorescence of the dye with the concentration of said contaminants; (b) adding one or more chemicals to said papermaking process that decrease the amount of said hydrophobic contaminants; and (c) re-measuring the amount of contaminants in said papermaking process by performing step (a) at least one more time; and (d) optionally controlling the amount of said chemicals that are added to said papermaking process.
  • The present invention also provides for a method of monitoring one or more types of hydrophobic contaminants in a papermaking process consisting essentially of: (a) obtaining a bulk sample of fluid from said papermaking process; (b) selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; (c) adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; (d) measuring the fluorescence of the dye in said fluid; (e) correlating the fluorescence of the dye with the concentration of said contaminants; and (f) optionally controlling the amount of one or more chemicals that reduce or inactivate said contaminants which are added to said papermaking process.
  • DETAILED DESCRIPTION OF THE INVENTION
  • “Papermaking process” means a method of making any kind of paper products (e.g. paper, tissue, board, etc.) from pulp comprising forming an aqueous cellulosic papermaking furnish, draining the furnish to form a sheet and drying the sheet The steps of forming the papermaking furnish, draining and drying may be carried out in any manner generally known to those skilled in the art. The papermaking process may include a pulping stage, e.g. making pulp from woody raw material and bleaching stage, e.g. chemical treatment of the pulp for brightness improvement. Furnishes can contain fillers and/or other contaminants.
  • “Bulk sample” means a sample whose constituents have not been specifically separated, except bulk sample may include, a separation based upon size. For example, bulk sample does not include separating e.g. a resin particle from a suspension.
  • “Fluid” includes an aqueous papermaking suspension from a papermaking process, e.g. a fluid containing fibers in a pulping stage, a thin stock, a thick stock, aqueous suspensions drawn from the papermaking process, e.g. various locations from a papermaking machine or pulping process, aqueous fluid in a uhl box, press dewatering section, and/or any part of the papermaking process that one of ordinary skill in the art can think of where one would need to monitor hydrophobic contaminants.
  • As stated above, the present invention provides for a method of monitoring one or more types of hydrophobic contaminants in a papermaking process via the use of fluorescence.
  • The dyes, which are added to the sample must be able to stain or interact with the hydrophobic contaminants, e.g. pitch particles.
  • In another embodiment, the turbidity of the fluid is also measured. In a further embodiment, the turbidity of said fluid is measured before and after the addition of said chemicals.
  • In another embodiment, the fluid is filtered or diluted or a combination thereof prior to said addition of said dye or said fluorescent measurement of said dye, wherein said filtering or dilution of said fluid permits said fluid to be fluorometrically monitored.
  • In another embodiment, the sample is taken from a dilute sample point off a papermaking process, e.g. a paper machine. In a further embodiment, the sample point is the white water of a papermaking process. The reasoning postulated for this collection/sample point is that there is no long fiber present/substantially any fiber present, and filtration may not be necessary.
  • In another embodiment, one or more samples undergo a sieving/separation step to separate the long fiber from the suspended contaminants in a sample solution. For example, the degree of dilution that the filtrate/aqueous fraction undergoes from the separation process relies on two main factors, both relating to turbidity. If the filtrate/aqueous fraction is too turbid for the turbidimeter, dilution is required to bring the turbidity into a measurable range for the meter. This is the case unless you want a less accurate and “quick and dirty” test, which is one embodiment of the claimed invention.
  • In another embodiment, if the turbidity is above 2000 NTU (nephelometric turbidity units), then it is a preferred embodiment that a sample from a papermaking process is diluted/further separated prior to the addition of a dye and fluorescent measurement. The value of 2000 NTU may be instrument or measurement technique dependent.
  • In another embodiment, the fluid is an aqueous filtrate of a pulp slurry.
  • In another embodiment, the dye does not include N-(n-butyl)4-(n-butylamino)-naphthalimide.
  • In another embodiment, the fluid is obtained from a wet end of said papermaking process.
  • As stated above, the dye added to a sample must have a sufficient amount of time for said dye to interact with said contaminants in said fluid prior to its fluorescent measurement. One of ordinary skill in the art could determine a sufficient amount of time for said interaction without undue experimentation.
  • In one embodiment, the dye is mixed with a solvent prior to its addition to said fluid. One of ordinary skill in the art could determine an adequate time for mixing without undue experimentation.
  • In another embodiment, the contaminants are selected from the group consisting of: pitch, fiber, filler, fines, coated broke, mill broke, recycle, groundwood, thermal mechanical pulp, chemi-thermal mechanical pulp, chemical pulp, deinked pulp, ink, adhesives, stickies, tackies, waxes, binders and dissolved and/or colloidal substances, and a combination thereof.
  • In another embodiment, the method is an on-line method and/or batch sample method.
  • In another embodiment, the fluorometric measurement is performed at a pre-set basis, intermittent basis, and/or continuous basis. For example, a flow cell can be utilized as a means for measuring the fluorescence of said hydrophobic contaminants. More specifically, in one embodiment, a process for measurement comprises: the addition of one or more fluorescent tracers to a sample obtained from a papermaking process prior to its fluorescent measurement in said flow cell. One of ordinary skill in the art would be able to carry out this process without undue experimentation. For example, one could utilize flow injection analysis and/or sequence injection analysis techniques to carry out the above-referenced measurement protocol.
  • In another embodiment, the fluorometric measurement is performed with a handheld fluorometer. A fluorescent measurement may be carried out with other types of fluorometers.
  • The present invention also provides for a method of measuring the effectiveness of one or more chemicals that decrease the amount of one or more hydrophobic contaminants in a papermaking process. The information on the amount of hydrophobic contaminants in a fluid can be utilized to form a control loop for the addition of one or more chemicals, which can be used to control the amount of hydrophobic contaminants.
  • In one embodiment, the methodology for monitoring the hydrophobic contaminants can be measured by the above-stated fluorescence methodology and its various embodiments.
  • In another embodiment, a determination of the amount of fluorescence is measured by the above-mentioned protocol, then subsequent to this step, an addition of one or more chemicals to the papermaking process to treat the hydrophobic contaminants, e.g. increase/decrease in the same chemistry for hydrophobic contaminant inhibition or change in the chemistry treatment program for hydrophobic contaminant inhibition, and then subsequent to the treatment step, a re-measurement of the amount of contaminants in said papermaking process by the above-mentioned protocol.
  • In another embodiment, the chemicals are at least one of the following: a fixative; a detackifier; a dispersant; a surfactant; and a retention aid.

Claims (15)

1. A method of monitoring one or more types of hydrophobic contaminants in a papermaking process comprising:
a. obtaining a bulk sample of fluid from said papermaking process;
b. selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid;
c. adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid;
d. measuring the fluorescence of the dye in said fluid;
e. correlating the fluorescence of the dye with the concentration of said contaminants; and
f. optionally controlling the amount of one or more chemicals that reduce or inactivate said contaminants which are added to said papermaking process.
2. The method of claim 1 further comprising: measuring the turbidity of said fluid.
3. The method of claim 2 wherein said turbidity of said fluid is measured before and after the addition said chemicals.
4. The method of claim 1, wherein said fluid is filtered or diluted or a combination thereof prior to said addition of said dye or said fluorescent measurement of said dye.
5. The method of claim 1, wherein said dye does not include N-(n-butyl)-4-(n-butylamino)-naphthalimide.
6. The method of claim 1 wherein said fluid is obtained from a wet end of said papermaking process.
7. The method of claim 1 wherein said dye is mixed with a solvent prior to its addition to said fluid.
8. The method of claim 1, wherein said contaminants are selected from the group consisting of: pitch, fiber, filler, fines, coated broke, mill broke, recycle, groundwood, thermal mechanical pulp, deinked pulp furnish, chemi-thermal mechanical pulp, chemical pulp, ink, adhesives, stickies, tackies, waxes, binders and dissolved and/or colloidal substances, and a combination thereof.
9. The method of claim 1, wherein said method is an on-line method and/or batch sample method.
10. The method of claim 1, wherein said fluorometric measurement is performed at a pre-set basis, intermittent basis, and/or continuous basis.
11. The method of claim 1, wherein said fluorometric measurement is performed with a handheld fluorometer.
12. The method of claim 1, wherein said fluid is an aqueous filtrate of a pulp slurry.
13. A method for measuring the effectiveness of one or more chemicals that decrease the amount of one or more hydrophobic contaminants in a papermaking process:
a. monitoring one or more types of contaminants in a papermaking process comprising: obtaining a bulk sample of fluid from said papermaking process; selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid; adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid; measuring the fluorescence of the dye in said fluid; and correlating the fluorescence of the dye with the concentration of said contaminants;
b. adding one or more chemicals to said papermaking process that decrease the amount of said hydrophobic contaminants; and
c. re-measuring the amount of contaminants in said papermaking process by performing step (a) at least one more time; and
d. optionally controlling the amount of said chemicals that are added to said papermaking process.
14. The method of claim 13, wherein said chemicals are at least one of the following: a fixative; a detackifier; a dispersant; a surfactant; and a retention aid.
15. A method of monitoring one or more types of hydrophobic contaminants in a papermaking process consisting essentially of:
a. obtaining a bulk sample of fluid from said papermaking process;
b. selecting a hydrophobic dye that is capable of interacting with said contaminants in said fluid and fluorescing in said fluid;
c. adding said dye to said fluid and allowing a sufficient amount of time for said dye to interact with said contaminants in said fluid;
d. measuring the fluorescence of the dye in said fluid;
e. correlating the fluorescence of the dye with the concentration of said contaminants; and
f. optionally controlling the amount of one or more chemicals that reduce or inactivate said contaminants which are added to said papermaking process.
US12/405,797 2009-03-17 2009-03-17 Use of fluorescence to monitor hydrophobic contaminants in a papermaking process Abandoned US20100236732A1 (en)

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US12/405,797 US20100236732A1 (en) 2009-03-17 2009-03-17 Use of fluorescence to monitor hydrophobic contaminants in a papermaking process
TW099105147A TW201035538A (en) 2009-03-17 2010-02-23 Use of fluorescence to monitor hydrophobic contaminants in a papermaking process
ARP100100747A AR075742A1 (en) 2009-03-17 2010-03-11 USE OF FLUORESCENCE TO MONITOR HYDROPHOBIC POLLUTANTS IN A PAPER MANUFACTURING PROCESS
PCT/US2010/027391 WO2010107731A1 (en) 2009-03-17 2010-03-16 Use of fluorescence to monitor hydrophobic contaminants in a papermaking process

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20160245757A1 (en) * 2013-09-29 2016-08-25 Ecolab Usa Inc. A Method of Controlling Hydrophobic Contaminants by Utilizing a Fluorescent Dye
US9562861B2 (en) 2011-04-05 2017-02-07 Nalco Company Method of monitoring macrostickies in a recycling and paper or tissue making process involving recycled pulp

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20130078730A1 (en) * 2011-09-23 2013-03-28 Michael J. Murcia Method for monitoring and control of a wastewater process stream
CN103743610A (en) * 2014-01-16 2014-04-23 陕西科技大学 Method for detecting content of micro-stickies in paper pulp
ES2955184T3 (en) * 2017-11-21 2023-11-29 Solenis Tech Lp Method of measuring contaminants in a pulp slurry or papermaking system

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5246547A (en) * 1992-07-14 1993-09-21 Nalco Chemical Company Hydrophobic polyelectrolyte coagulants for the control of pitch in pulp and paper systems
US5486904A (en) * 1990-12-18 1996-01-23 Basf Aktiengesellschaft Method for determining resin particles in paper stocks
US5940177A (en) * 1997-01-10 1999-08-17 Basf Aktiengesellschaft Method and apparatus for determining the size distribution of different types of particles in a sample
US20090084510A1 (en) * 2007-05-16 2009-04-02 Buckman Laboratories International, Inc. Methods To Detect Organic Contaminants In Pulp and Fiber
US20100012284A1 (en) * 2007-03-01 2010-01-21 Basf Se Method for determining hydrophobic organic particles in a paper stock

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7909963B2 (en) * 2006-01-18 2011-03-22 Cascades Canada Inc. Method for measuring hydrophobic contaminants in paper pulp

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5486904A (en) * 1990-12-18 1996-01-23 Basf Aktiengesellschaft Method for determining resin particles in paper stocks
US5246547A (en) * 1992-07-14 1993-09-21 Nalco Chemical Company Hydrophobic polyelectrolyte coagulants for the control of pitch in pulp and paper systems
US5940177A (en) * 1997-01-10 1999-08-17 Basf Aktiengesellschaft Method and apparatus for determining the size distribution of different types of particles in a sample
US20100012284A1 (en) * 2007-03-01 2010-01-21 Basf Se Method for determining hydrophobic organic particles in a paper stock
US20090084510A1 (en) * 2007-05-16 2009-04-02 Buckman Laboratories International, Inc. Methods To Detect Organic Contaminants In Pulp and Fiber

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9562861B2 (en) 2011-04-05 2017-02-07 Nalco Company Method of monitoring macrostickies in a recycling and paper or tissue making process involving recycled pulp
US20160245757A1 (en) * 2013-09-29 2016-08-25 Ecolab Usa Inc. A Method of Controlling Hydrophobic Contaminants by Utilizing a Fluorescent Dye
JP2016535244A (en) * 2013-09-29 2016-11-10 エコラブ ユーエスエイ インク Method for controlling hydrophobic contaminants by using fluorescent dyes

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