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Impact of Film-Forming Amines on the Reliability of Online Analytical Instruments Marco Lendi

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  • 8/18/2019 Impact of Film-Forming Amines on the Reliability of Online Analytical Instruments Marco Lendi

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     AMI INSPECTOR AMI Sodium P

    Conductivity with Case

    PowerPlant Chemistry SPECIAL PRINT (2014) PowerPlant Chemistry 2012, 14(9)

        S    P    E    C    I    A    L    P

        R    I    N

        T Impact of Film-Forming Amines on the Reliabilityof Online Analytical Instruments

    Marco Lendi

    Dr. Peter Wuhrmann

    SWAN Analytische Instrumente AG, 8340 Hinwil/Switzerland

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     ANALYTICAL INSTRUMENTS

    SWAN  Analytische Instrumente AG · 8340 Hinwil/Switzerland 

    n  Fully Automated Sodium Analyzer

    · Automatic 3-point known addition

    calibration in ppb-range· Automatic regeneration of sodium

    electrode

    · Automatic control loop for sample

     pH conditioning

    n  Lowest detection limit for sodium

     ion concentration: 0.001 ppb

    n  Factory tested and ready for

     installation and operation.

     Ask for technical documentation or

    check our homepage

    Made in Switzerland 

    www.swan.ch

     AMI Soditrace -  On-line analyzer for the continuous measurement of sodium ions in

    trace amounts in steam and high purity water.

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    PPChem

    1PowerPlant Chemistry 2012, 14(8)

    Impact of Film-Forming Amines on the Reliability of Online Analytical Instruments

    INTRODUCTION

    Organic additives like oxygen scavengers or film-forming

    amines (FFA) are widely used in small industrial water-

    steam cycles, and their use in larger installations is sug-

    gested more and more frequently. Hardly any reports

    describe their influence on the online monitoring system,

    and their impact on specific parameters has never been

    reviewed properly [1].

     A field test in a waste incineration plant [2] showed signifi-cant coating effects on conductivity and oxygen probes.

    With the test methods available in the field, no negative

    effects on pH and sodium probes could be measured. But

    to draw a final conclusion, the recorded data showed too

    many pattern noises coming from the operation mode of

    the plant. Furthermore, in this field test only one FFA prod-

    uct was involved.

    This situation was the main motivation to repeat the test in

    a controlled laboratory-like installation with as few disturb-

    ing effects as possible. Additionally, the tests were per-

    formed with three different brands of film-forming amines

    to give more relevant results.

    ONLINE TEST SYSTEM

    The flow scheme is shown in Figure 1. The raw water was

    purified by reverse osmosis, mixed-bed ion exchange and

    UV disinfection to obtain ultrapure water (UPW). Table 1

    lists the average specifications of the UPW.

    Oxygen Removal

    The oxygen level could be reduced from saturation

    (8 mg · L–1 ) to below 10 µg · L–1 with three Liqui-Cel®

    Membrane Contactors connected in series. For a reduc-

    tion to 10 µg· L–1 O2 the contactors were evacuated with

    Impact of Film-Forming Amines on the Reliability of 

    Online Analytical Instruments

    © 2012 by Waesseri GmbH. All rights reserved.

     ABSTRACT

    There are very few reports describing the effects of the dosing of film-forming amines (FFAs) on the online monitoring

    equipment. This paper describes controlled, laboratory-like tests performed to ascertain the impact of three different

    brands of film-forming amines on system parameters. Specific conductivity, pH drift, cation resin retention, pH stabil-

    ity, sodium step response, sodium calibration, oxygen sensor response and ORP probe response were considered.

    While with some measurements no negative influence could be observed, with other equipment there was a loss of

    sensitivity and speed of response time due to coating effects. There were also differences in some results depending

    on the FFA used.

    Marco Lendi and Peter Wuhrmann

    NaCl/NH

    addition3   FFA

    addition

    Input

    UPW

    Oxygen

    removal

    Exposed

    instruments

    Referenceinstruments

    Figure 1:

    Flow scheme of the test system.

    Parameter Range

    Sodium 0.01–0.02 µg · L–1

    Silica 0.1 µg · L–1

    Conductivity 0.055–0.057 µS · cm–1

    Oxygen Oxygen saturated (8–9 µg · L–1 )

    Table 1:

     Average specifications of the input ultrapure water.

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    PPChem Impact of Film-Forming Amines on the Reliability of Online Analytical Instruments

    high vacuum and purged with nitrogen. In this way it was

    possible to keep a stable oxygen level below 10 µg · L–1 for

    hours. The oxygen was only reduced for a short period to

    test the oxidation-reduction potential (ORP) and the oxy-

    gen probe's response while the other data was recorded

    with saturated oxygen levels.

    Dosing Points

    Dosing was designed for a flow-dependent addition such

    that a constant concentration of a given substance could

    be maintained over several days. The first dosing point

    was used to dose sodium chloride solution and/or ammo-

    nia. With the second dosing point, the film-forming amines

    (FFA) were dosed. The reference instruments were

    mounted upstream of the second dosing point, so that

    these instruments were never exposed to film-forming

    amines.

    Online Instruments

    The complete list of the tested instruments is given in

    Table 2.

    Test Procedures and Materials

    Phase 1: Recording of the base line

    During this phase, no FFA was dosed. Tests like

    sodium step responses or oxygen reductionwere performed to see the instruments reaction

    under laboratory conditions.

    Phase 2: Dosing of a small amount of FFA 

     A target concentration of 0.5 mg · L–1 as FFA 

    was dosed. The goal of this phase was to

    observe possible effects with low FFA concen-

    tration.

    Phase 3: Verification stage

    The dosing of FFA was interrupted, perfor-

    mance tests were continued. This phase gave

    an impression of the irreversibility of the coating

    effects.

    Phase 4: High concentration FFA dosing

    Target concentrations up to 3 mg · L–1 as FFA 

    were dosed. Depending on brand and applica-

    tion, these are the recommended concentra-

    tions of the manufacturers.

    Three commonly used film-forming amine brands were

    tested. In the following report, the names as well as the

    manufacturers have been made anonymous. The shown

    FFA concentrations were calculated based on the flow-

    dependent addition and were frequently measured with

    the available test methods of the used products.

    TEST RESULTS

    Conductivity Probe

    The installed conductivity probes on the AMI Deltacon DGare titanium 2-electrode types with a cell constant of

    0.04 cm–1 and an integrated PT1000 temperature sensor.

    Instruments Parameter Sample

    Specific conductivity

     Acid conductivity AMI Deltacon DG

    Degassed acid conductivity Reference instruments

    Calculated pH

     AMI Sodium P SodiumSpecific conductivity

     Acid conductivity AMI Deltacon DG

    Degassed acid conductivity

    Calculated pH

     AMI pH Ion selective pH Exposed instruments

     AMI ORP Oxidation-reduction potential

     AMI Soditrace Trace sodium

     AMI Oxytrace QED Trace oxygen with online verification

     AMI Sodium A Sodium

    Table 2:

    Online instruments and parameters.

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    Points of interest were:

    (1) Coating effects on specific conductivity (SC) probe

    (2) Drift between pH calculation and ion selective meas-

    urement

    (3) Retention capacity of the cation exchange resin

     A summary of the impact of the FFAs tested on specific

    conductivity, pH drift, and cation resin retention is given in

    Table 3.

    Coating Effects on Specific Conductivity Probe

    This sensor is in direct contact with the FFA. The acid con-

    ductivity and the degassed acid conductivity sensors are

    protected by the cation exchange resin. Of the three

    tested brands, only one substance did not decrease the

    specific conductivity compared with acid and degassed

    acid conductivity.

    Two criteria were established to detect a coating effect:

    • Decrease in specific conductivity

    (SC) compared with degassed acid

    conductivity (DC) during FFA dos-

    ing;

    • Lower specific conductivity values

    of the exposed instrument com-

    pared with the reference after a

    longer period of FFA dosing.

    Figure 2 shows the behavior of the SCwith FFA no. 3. The FFA concentration

    of substance no. 3 was 1 mg · L–1

    during the whole measuring period. At

    the beginning, the SC reading was

    17.38 µS · cm–1, then it dropped to

    14.58 µS · cm–1. The decrease of

    2.06 µS · cm–1 within three days is

    clearly an indication of coating on the

    conductivity probe. This is supported

    by the observation that during the

    same period the degassed acid con-

    ductivity (DC) is more or less constant

    between 0.143 and 0.164 µS · cm–1.

    Figure 3 shows the coating effect of FFA no. 2. After a

    three-day exposure time at 1 mg · L–1 FFA, a step

    response with a target concentration of 100 µg · L–1

    sodium was performed. The readings of the non-exposed

    reference conductivity probe and the exposed sensor

    were compared.

     At the beginning, the reading of the exposed sensor is0.489 µS · cm–1, which is considerably lower than the SC

    of the reference instrument (0.513 µS · cm–1 ). Figure 3 also

    shows that the coating effect disappeared about half an

    hour after the FFA dosing was stopped.

    Difference between pH Calculation and Ion Selective

    Measurement  According to VGB-450L [3], the pH of

    a sample can be calculated with the specific and acid

    conductivity. As shown previously, the specific conductiv-

    ity sensors are coated by two of the three film-forming

    amines. As a result, the calculated pH should alsodecrease compared to the ion selective measurement with

    a glass electrode.

    FFA no. 1 FFA no. 2 FFA no. 3

    Coating on SC probe No Yes Yes

    pH drift No No Yes

    Retention capacity Poor Poor Poor

    Table 3:

    Summary of results on specific conductivity, pH drift, and resin retention.

    50

    40

         C    o    n     d    u    c     t     i    v     i     t    y     [    µ     S

        c    m

         ]

       ·

      –     1

    Time [day]

    0 1 2 3

    30

    20

    100.5

    0.4

    0.3

    0.2

    0.1

    Specific conductivity (SC)

    Degassed acid conductivity (DC)

    Figure 2:

    Coating of specific conductivity (SC) probe during an exposure to 1 mg · L–1 of FFA 

    no. 3.

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    In Figure 4 the deviation between the

    calculated and measured pH during

    FFA no. 3 dosing is shown as pH.

    Over a three-day exposure time, the

    deviation was –0.10 pH. Another

    piece of evidence for the 'coating the-ory' is the fact that in the shown time

    the ion selective measured pH (sepa-

    rated measuring and reference elec-

    trode) is not drifting.

     A coating-like behavior of FFA no. 2

    could be demonstrated with a step

    response, but the measured deviation

    was much lower than the one from

    FFA no. 3. The influence on pH calcu-

    lation was too small to demonstrate a

    significant drift.

    Retention Capacity of the Cation

    Exchange Resin

    The quality of the cation exchange

    resin is a key factor in measuring a

    reliable and stable acid and degassed

    acid conductivity. The resin utilized

    was a strongly acidic cation

    exchanger in H+ form. Under normal

    operation, the tested resin will hold

    back ammonia-treated water for

    approximately 1 month before theresin is exhausted.

    The dosed FFA substances contain

    not only the film-forming amines.

     According to the Material Safety Data

    Sheets of the tested substances, the

    mixtures contain a high load of other

    cationic molecules. Figure 5 shows

    the beginning of a dosing (phase 2)

    with a low concentration of FFA no. 1.

     After three days, it seems that the

    cation exchange resin cannot holdback all cationic substances because

    the degassed acid conductivity (DC)

    of the exposed instrument is begin-

    ning to rise. Figure 6 shows the con-

    tinued test with FFA no. 1 after 44

    days of exposure. After the dosing of

    FFA no. 1 was stopped, the DC of the

    exposed instrument remained on a

    high level. It seems that the cation

    exchange resin is continuing to release ionic substances.

    The DC reading went back to normal after a new bottle of

    resin was installed. This is the proof that the source of the

    ionic substances responsible for the higher DC readings

    was the cation exchange resin.

    FFAs no. 2 and no. 3 gave the same picture. The only dif-

    ference between the substances was the time until ionic

    substances broke through.

         C    o    n     d    u    c     t     i    v     i     t    y     [    µ     S

        c    m

         ]

       ·

      –     1

    SC reference instrument

    SC exposed instrument

    Dosing of NaCl

    Dosing of FFA

    0.7

    0.6

    0.5

    0.4

    0.3

    0.2

    0.1

         N    a     D    o    s     i    n    g     [    m    g

         k    g

         ]

       ·

      –     1

    0.5

    0.4

    0.3

    0.2

    0.1

    0

    2.5

    2.0

    1.5

    1.0

    0.5

    0

    00:00 00:30 01:00 01:30

    Time [hh:minmin]

         F     F     A     D    o    s     i    n    g     [    m    g

         k    g

         ]

       ·

      –     1

    Figure 3:

    Step response with a sodium chloride solution after a FFA dosing period (substance

    no. 2) to compare the specific conductivity (SC) reading of the exposed and reference

    instrument.

               p       H

    pH

    Control line

    Calculated pH

    Ion selective measured pH

    0.8

    0.6

    0.4

    0.2

    0

     –0.2

     –0.4

         p       H

    11

    10

    9

    8

    7

    0

    Time [day]

    0.5 1.0 1.5 2.0 2.5 3.0

    Figure 4:

    Drift between the calculated and ion selective measured pH (1 mg · L–1 FFA no. 3).

    Impact of Film-Forming Amines on the Reliability of Online Analytical Instruments

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    pH/Sodium (Ion Selective Glass

    Electrode)

    The installed sodium reference instru-

    ment was an AMI Sodium P and the

    exposed sodium probes were on an

     AMI Soditrace. On both instruments,

    the same types of measuring and ref-

    erence electrodes were used. The ref-

    erence electrode was a calomel

    (Hg/HgCl) electrode with a KCl liquid

     junction.

    The installed pH electrode used a sep-

    arated reference electrode system

    based on Ag/AgCl with a KCl liquid

     junction.

    Points of interest were:

    (1) pH: stability during long-term

    exposure

    (2) Sodium: reaction time during step

    response

    (3) Sodium: calibration data

    Table 4 shows a summary of the test

    results.

    pH Stability  Figure 7 shows a 10-day exposure period with FFA no. 1.

    The stability during that test was

    good, and the response to changes in

    FFA concentrations was fast and

    reversible. Therefore, no negative

    influence could be noticed.

    Sodium Step Response The nor-

    mal sodium level during the test was

    between 0.02 µg · L–1 and 0.10 µg· L–1

    sodium. The sensors were regener-

    ated weekly with a sodium-free etch-ing solution. With flow-dependent

    injection of a sodium chloride solution,

    a 'contamination' of 200 µg · L–1 Na

    DC of reference instrument

    DC of exposed instrument

    FFA dosing

    1.0

    0.5

    2.0

    1.5

    1.0

    0.5

    0

    0

    Time [day]

    2 4 6 8

    0.1

    0.05

         C    o    n     d    u    c     t     i    v     i     t    y     [    µ     S

        c    m

         ]

       ·

      –     1

         F     F     A     D    o    s     i    n    g     [    m    g

         k    g

         ]

       ·

      –     1

    Figure 5:

    Retention capacity of cation exchange resin with respect to the degassed acid

    conductivity (DC) during a dosing period of FFA no. 1.

    DC of reference instrument

    DC of exposed instrument

    FFA dosing

    1.0

    0.5

    5.0

    4.0

    3.0

    2.0

    1.0

    0

    44

    Time [day]

    46 48 50 54

    0.1

    0.05

         C    o    n     d    u    c     t     i    v     i     t    y     [    µ     S

        c    m

         ]

       ·

      –     1

         F     F     A     D    o    s     i    n    g     [    m    g

         k    g

         ]

       ·

      –     1

    52

    New cationexchange resin

    Figure 6:

    Retention capacity of cation exchange resin with respect to the degassed acid

    conductivity (DC) after a dosing period of FFA no. 1.

    FFA no. 1 FFA no. 2 FFA no. 3

    pH stability No influence No influence No influence

    Sodium step response No influence No influence No influence

    Sodium calibration No influence –– –

    Table 4:

    Summary of results on pH stability, sodium step response, and sodium calibration.

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    was simulated. The most important

    parameter to evaluate the perfor-

    mance of an ion selective sodium sen-

    sor is the response time to concentra-

    tion changes. Figure 8 summarizes

    five step responses during long-termexposure to different concentrations

    of FFA no. 1. No significant loss of the

    sodium probe's response time can be

    observed.

    Oxygen and ORP Sensor

    For direct oxygen measurement a

    Clark oxygen sensor with a gold cath-

    ode and silver anode was used.

     Additionally, a Faraday electrode for

    online verification was built in.

    The ORP was measured with a sepa-

    rated platinum (Pt) measuring elec-

    trode and reference electrodes with a

    KCl liquid junction were used.

    Points of interest were:

    (1) Clark probe: response time during

    oxygen concentration reduction

    (2) ORP probe: response time during

    oxygen concentration reduction

    Response Time of Oxygen and ORP

    Probes to Oxygen Concentration

    Changes The long-term

    stability tests were performed with

    oxygen saturated ultrapure water

    (8 mg· L–1O2 ). To test the oxygen and

    ORP probes' performance, oxygen

    was removed (see Figure 1) from the

    sample water. The oxygen concentra-

    tion of the water during removal was

    the same. Table 5 shows a summary of

    the test results.

    FFA no. 1 FFA no. 2 FFA no. 3

    Oxygen response time Good Good Good

    ORP response time Bad Bad Bad

    Table 5:

    Summary of results on oxygen sensor response and ORP response.

        p     H

    12

    11

    10

    9

    8

    7

    6

    10

    8

    6

    4

    2

    0

    0Time [day]

    2 4 6 8 10 12

         F     F     A     D    o    s     i    n    g     [    m    g

         k    g

         ]

       ·

      –     1

    pH

    FFA dosing

    Figure 7:

    Long-term stability of ion selective pH probe during dosing of FFA no. 1.

    300

    250

    200

    150

    100

    50

    0

    0.00

    Time [h]

    0.01 0.02 0.03 0.04

    3 days (0.5 mg kg FFA)

    12days (1 mg kg FFA)

    20days (0 mg kg FFA)

    40days (2 mg kg FFA)

    49days (4 mg kg FFA)

    ·

    ·

    ·

    ·

    ·

     –1

     –1

     –1

     –1

     –1

          N     a

          [     µ     g

          k     g

          ]

        ·

       –      1

    Figure 8:

    Recorded step responses from an AMI Soditrace during long-term exposure to FFA 

    no. 1.

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    PPChemImpact of Film-Forming Amines on the Reliability of Online Analytical Instruments

    Figure 9 shows three examples of ORP

    responses during different FFA dosing

    phases. The ORP readings in Figure 9

    are standardized because the FFA 

    concentration itself also influences the

    ORP value. The red line (0.5 mg · L–1 )shows an ORP response after a 5-day

    period of FFA dosing while the green

    l ine (1 mg · L–1 ) was recorded after a

    13-day dosing period.

    No alteration of the Clark sensor char-

    acteristics was observed under any of

    the conditions tested in these experi-

    ments (Figure 10).

    CONCLUSION

    The impact of three different condition-

    ing reagents containing film-forming

    amines on online instrumentation was

    tested in a laboratory-like installation.

    On pH, ion selective sodium measure-

    ment as well as on a Clark-type oxy-

    gen probe, no negative influence could

    be observed. On oxygen reduction

    potential (ORP) measurement, alltested FFA substances result in a loss

    of sensitivity and speed of response

    time due to coating effects. The impact

    on conductivity measurement differed

    between the tested substances. With

    two tested substances, coating effects

    on the conductivity probe could be

    observed which resulted in a drift of

    the specific conductivity reading as

    well as in a drift of the calculated pH.

    With one film-forming amine product,

    such effects could not be observed.

         O     R     P     [    m     V     ]

    20

    0

     –20

     –40

     –60

     –80

     –100

     –120

     –140

     –160

     –180

    8 000

    6 000

    4 000

    2 000

    0

    00:00

    Time [day]

    00:20 00:40 01:00   01:20   01:40

         O

         [    µ    g

         k    g

         ]

         2

      –     1

       ·

    0 mg k g FFA

    0.5mg kg FFA

    1 m g kg FFA

    Oxygen level

    ·

    ·

    ·

     –1

     –1

     –1

    Figure 9:

    Reaction of an ORP probe during oxygen removal with different FFA concentrations of

    FFA no. 1.

    200

    150

    100

    50

    0

    1.2

    1.0

    0.8

    0.6

    0.4

    0.2

    0

    0

    Time [day]

    2 4 6 8 10 12

         F     F     A     D    o    s     i    n    g     [    m    g

         k    g

         ]

       ·

      –     1

    FFA concentration

    O level2

         O

         [    µ    g

         k    g

         ]

         2

      –     1

       ·

    14 16

    Figure 10:

    Response of a Clark oxygen probe during FFA dosing (FFA no. 1).

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    REFERENCES

    [1] Verheyden, K. S., Ertryckx, R. A. M., De Wispelaere,

    M., Poelemans, N., PowerPlant Chemistry 2003, 5(9),

    516.

    [2] Lendi, M., Wuhrmann, P., EPRI Major Component Reliability Meeting, 2011 (Barcelona, Spain). Paper

    #16.

    [3] VGB Guideline for Boiler Feedwater, Boiler Water and 

    Steam of Steam Generators with a Permissible

    Operating Pressure of > 68 bar , 1988. VGB Power

    Tech e.V., Essen, Germany, VGB-R 450-Le.

    THE AUTHORS

    Marco Lendi (B.S., Chemistry, University of Applied

    Science, Zurich, Switzerland) joined Swan Analytical

    Instruments in 2009, working first as a quality manager

    and from 2010 in SWAN's customer support group. In

    2012 he was promoted to the R&D group.

    Peter Wuhrmann (Ph.D., Analytical Chemistry, Swiss

    Federal Institute of Technology (ETHZ), Zurich, Switzer-

    land) conducted several years of research work with ion

    sensitive microelectrodes for intracellular ion measure-

    ments at the Institute of Cell Biology at the Swiss Federal

    Institute of Technology (ETHZ). He was a member of thefounding group of Swan Analytical Instruments, where he

    has been responsible for R&D since 1991.

    CONTACT

    Marco Lendi

    Swan Analytical Instruments AG

    P.O. Box 398

    8340 Hinwill

    Switzerland

    E-mail: [email protected]

    Dr. Peter Wuhrmann

    [email protected]

    Impact of Film-Forming Amines on the Reliability of Online Analytical Instruments

    Degassed Cation Conductivity 

     Analyzer AMI Deltacon DG

     ANALYTICAL INSTRUMENTS

    SWAN ANALYTISCHE INSTRUMENTE AG · CH-8340 HINWILwww.swan.ch · [email protected] · Phone +  4144 9436300

     Automatic and continuous

     measurement of total, cation and 

    degassed cation conductivity.

    Re-boiler according to Larson-

    Lane (ASTM D4519-94).

    Tightly controlled degassing

    temperature.

    Calculation of sample pH and 

     ammonia concentration.

     Ask for technical documentation

    or check our homepage.

    www.swan.ch

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     ANALYTICAL INSTRUMENTS

    n  Faraday electrode and control

    unit for the automatic verification

     by electrochemically generated

    oxygen in the ppb range

    n  Extension of the maintenance

     intervals: no calibration as long

     as the verification is valid 

    n  Sample flow monitoring with

     alarm «Flow out of range»

    n  Easy maintenance due to

     sensor cap concept.

    Made in Switzerland 

     AMI Oxytrace QED -  Dissolved oxygen in high purity water

    with integrated autoverification.

    Your notes:

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    SWAN  Analytische Instrumente AG

    www.swan.ch · Hinwil/Switzerland 

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