2015 11 06 -- Cetamine Technology in Power Plants - Swedish Conference 2015

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    INTRODUCTION

    THE CETAMINE

    TECHNOLOGY

    FILM FORMATION ON METAL SURFACES

    MAGNETITE LAYER STABILIZATION

    CETAMINE

    ANALYTICAL METHOD

    CASE STUDY I

    IMPACT ON CATIONIC CONDUCTIVITY

    CASE STUDY II

    DRY LAY-UP WITH CETAMINE

    REFERENCES AND CONCLUSIONS

    30/11/2015 2

    CONTENT

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    BOILER WATER ADDITIVES

    All-Volatile-Treatment (AVT) conceptspH adjustment realized by volatile alkalizing agents

    Treatment Concept Agent 1 Agent 2

    AVT-RVolatile Treatment for pH adjustment

    + Reducing agent

    Ammonia

    Alkalizing Amines

    Hydrazin

    CarbohydrazidDEHA

    AVT-O Volatile Treatment for pH adjustmentAmmonia

    Alkalizing Amines

    OT Volatile Treatment for pH adjustment+ FFA (Filmforming Amines) Ammonia Oxygen

    AVT-FVolatile Treatment for pH adjustment

    + FFA (Filmforming Amines)

    Alkalizing Amines

    AmmoniaFFA

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    CetamineTechnology

    4

    BOILER WATER ADDITIVES

    AlkalisingAmines

    Film Forming Amines

    All-in-oneproduct concept

    to treat thewhole

    water steamcycle

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    R1-

    NH-R2-n-NH2

    R1 is an unbranched alkyl chain with 12 to 18 carbon atoms

    R2 is a short-chain alkyl group with usually 1 to 4 carbon atoms

    n is between 0 and 7

    CETAMINE

    FILMING AMINE CFA)

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    Film formation on metal surfaces

    Magnetite layer stabilization

    Improved heat transfer

    Compatibility with online sensors

    CetaminePhotometric Method

    Wet and dry lay-up of industrial systems

    Savings in energy and water

    6

    BENEFITS OF CETAMINE

    TECHNOLOGY

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    Adsorption and Formation of a Protective

    Film on Metal Surfaces

    Hydrophobic Barrier between Water andMetal

    1 1 1

    2 2

    3 3

    1. Adsorption

    2. Ion - ion

    3. Hydrophobic bond

    FILM FORMATION ON METAL SURFACES

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    Cetamineuntreated

    Protective Film

    Metal

    Molecules in water phase

    8

    FILM FORMATION ON METAL SURFACES

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    CetamineTreatment

    - low micro roughness

    - homogeneous surface

    Tradit ion al Treatment

    - high micro roughness

    - inhomogeneous surface

    9

    MAGNETITE LAYER STABILIZATION

    UNIVERSITY OF ROSTOCK, GERMANY

    Shell boiler simulation at university of Rostock at steady state

    conditions, p = 15 bar

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    a) PO4

    b) Cetamine V211

    (Different Scale)

    Cross SectionExamination

    of Tube Surfaces

    Cetamine Treatment

    Traditional Treatment

    15 um

    5 um

    MAGNETITE LAYER STABILIZATION

    UNIVERSITY OF ROSTOCK, GERMANY

    Shell boiler simulation at university of Rostock at steady stateconditions, p = 15 bar

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    Iron Oxide Layer Development in 90 bars Water-Tube Boiler, Paper Industry

    Acid pickling

    AmmoniaPhosphate

    FFA TreatmentCetamineV211

    CetamineV2100

    Internal limit at 500 g/m

    Online cleaning

    Acid picklingAcid pickling

    1According to ASTM 3483-05 Standard Test Methods for Accumulated Deposition in Steam Generator Tubes

    1

    MAGNETITE LAYER STABILIZATION

    PAPER INDUSTRY, ISRAEL

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    Compatibility of Cetamine with SWAN Online-Sensors

    Cetamine FFA product 2 FFA product 3

    Conductivity YES X X

    pH YES YES X

    Sodium YES YES YES

    Oxygen YES YES YES

    Full study was published by SWAN Analytical Instruments in

    PowerPlant Chemistry 2012, 14(9) Impact of Film-Forming Amines on

    the Reliability of Online Analytical Instruments

    Cetamine products are compatible with relevant online-sensors usedunder these test conditions

    12

    COMPATIBILITY WITH ONLINE SENSORS

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    CetamineTest Kit

    CetaminePhotometric Method

    CetamineMonitor

    13

    CETAMINE

    ANALYSIS

    CUSTOMIZED SOLUTIONS

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    Closed hot water systemsClosed cooling systems

    Industrial and district heating networks

    ClosedSystems

    APPROVED APPLICATIONS

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    Low to High Pressure Systems

    Power Plants (Turbines)Food Industry (Direct Food Contact)

    Alkaline Boiling-Out (VGB-S-513-00)

    Wet and Dry Lay-Up

    SteamGenerators

    APPROVED APPLICATIONS

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    CETAMINE

    - WASTE INCINERATION PLANT

    IMPACT ON CATIONIC CONDUCTIVITY

    30/11/2015 16

    CASE STUDY I

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    Plant: Waste Inceneration

    Type of system: Water-tube (CHP)

    Fuel: Refuse Derived Fuel (RDF)

    Rated Thermal Input: 48 MW

    Pressure: 42 bar

    Steam temperature: 400 C (after superheater)

    Steam production: 55 t/h

    Return of condensate: ca. 95 %

    Turbine manufacturer: MAN Turbo AG

    Type of turbine: Extraction condensing turbineMake-up: DI water

    Thermal Deaerator: T = 115 to 120 C

    Nehlsen Heizkraftwerke GmbH & Co. KG,Stavenhagen, Germany

    CETAMINE

    - WASTE INCINERATION PLANT

    THE PLANT

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    DI-water-

    tank

    SH3

    Feedwater

    Steam drum

    EC3EC2EC1

    Dosage of Cetamine V211

    Boiler SH2 SH1

    HPLP

    Consumer

    Town water

    Ion exchanger

    Reversed osmosis

    EDI

    Return of condensate ca. 95 %

    4 different condensates

    CETAMINE

    - WASTE INCINERATION PLANT

    GENERAL FLOW SCHEME

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    Steam on turbine VGB-S-010-T00AL 1 plant

    direct conductivity S/cm --- 5.8

    cationic conductivity S/cm 0.5 * 0.6

    degassed cat. cond. S/cm 0.2 0.4

    pH-value --- 9.4Na ppb < 5 ---

    Fe ppb < 20 < 20

    Cu ppb < 3 ---

    SiO2 ppb < 20 < 10CFA ppm --- 0.3

    * Higher action values may be defined if the increase of cationic conductivity can be attributed tocarbon dioxide and organic decomposition products can be excluded.

    CETAMINE

    - WASTE INCINERATION PLANT

    STEAM PARAMETERS

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    CETAMINE

    - WASTE INCINERATION PLANT

    DEGASSES CATIONIC CONDUCTIVITY

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    0,00

    0,10

    0,20

    0,30

    0,40

    0,50

    0,60

    0,70

    0,80

    16:33 18:57 21:21 23:45 2:09 4:33 6:57 9:21

    conductivity[S/cm]

    time [hh:mm]

    degassed acidic conductivity and CO2-contribution

    acidic

    conductivity

    degassed

    acidicconductivity

    ca. 16 h

    CO2

    CETAMINE

    - WASTE INCINERATION PLANT

    DEGASSES CATIONIC CONDUCTIVITY

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    LCOCDLiquid ChromatographyOrganic Carbon DetectionEt

    hanolamine

    Ammonia

    Glycol

    LMWA

    Cyclohexylamine

    concentrations of organiccompounds

    ppb C (carbon)

    concentrations of ammonia

    ppb N (nitrogen)

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    0,58

    0,18

    0,16

    0,12

    0,12

    0,0

    0,1

    0,2

    0,3

    0,4

    0,5

    0,6

    0,7

    0,8

    0,9

    1,0

    cationic conductivity

    measured

    single components

    calculated

    cationicconductivity/S/cm

    Estimation of contribution of single components to

    cationic conductivity

    water

    amines

    LMWA

    CO2

    0,06

    CETAMINE

    - WASTE INCINERATION PLANT

    THEORETICAL COMPOSITION OF CATIONIC CONDUCTIVITY

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    Combustion chamberfacing half-shell

    Combustion chamberaverting half-shell

    Compact topotactical oxide layer which is tightly bonded with

    the material.

    The magnetite coating is predominantly even with a thickness

    of

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    CETAMINE

    - WASTE INCINERATION PLANT

    MAN TURBO AG TURBINE EXAMINATION REPORT 2011

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    CETAMINE

    - WASTE INCINERATION PLANT

    MAN TURBO AG TURBINE EXAMINATION REPORT 2011

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    Cationic conductivity not in line withVGB-S-010-T-00

    Reasons have been investigated

    All other parameters in line with

    VGB-S-010-T-00

    Plant treated right from the start with

    Cetamine

    Inspected evaporator tubes in excellent

    condition according to VBG

    Inspected turbine in excellent condition

    according to MAN

    27

    CETAMINE

    - WASTE INCINERATION PLANT

    CONCLUSIONS

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    CETAMINE

    - BROWN COAL FIRED CHP PLANT

    DRY LAY-UP

    30/11/2015 28

    CASE STUDY II

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    Brown coal fired power plant (construction: 1999)

    Combined heat & power

    Supply of nearby city with

    District heat 90 MW

    Electricity 62 MW

    1 Gas turbine (ABB)

    1 HP steam turbine (ABB)

    1 IP/LP steam turbine (ABB)

    29

    DRY LAY-UP WITH FILM FORMING AMINES

    THE PLANT

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    Make-up water: DI-water

    Boiler pressure: 144 bar

    Steam temperature: 540 C (Superheater)

    Steam capcity: 205 t/h

    Cycle chemistry: AVT(O) (Ammonia)

    condensate pH: 8.8

    Condenser material: steel, brass

    Condensate polishing unit: Ion exchanger

    30

    DRY LAY-UP WITH FILM FORMING AMINES

    WATER/STEAM CYCLE CHARACTERISTICS

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    Acid conductivity: approx. 0.1 S/cm

    Fe (AAS graphite tube): < 2 g/L

    SiO2: < 5 g/L

    As of 2009 decrease of heat consumption

    Therefore, economic operation not possible during summer

    => Dry lay-up for 4 to 5 months necessary

    31

    DRY LAY-UP WITH FILM FORMING AMINES

    WATER QUALITY ACCORDING TO VGB-S-010

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    Conventional dry lay-up not satisfyingComplete emptying of units impossible

    (sagging tubes & parts)

    Plant not equipped for Nitrogen blanketing

    Start-up condensate contains high Fe levels(e.g. in 2011 ca. 50 to 90 g/L)

    Re-engineering of plant too expensive

    Dry lay-up with filmforming amines

    32

    DRY LAY-UP WITH FILM FORMING AMINES

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    1 month before shut down changeover from ammonia dosage to filmformig amine based product

    Dosage of undiluted product proportional to make-up water using same

    equipment

    By-passing of Condensate Polishing Unit

    Control parameter in main steam and condensate:

    FFA concentration > 0.2 and < 1 mg/L

    pH > 8.8

    Acid conductivity < 1 S/cm

    (additional measurement of degassed acid conductivity)

    Feeding of turbine with warm dried air during shut-down

    Restart of water/steam cycle with ammonia

    33

    DRY LAY-UP WITH FILM FORMING AMINES

    PROCEDURE

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    Parameter Unit Specification Measurement

    FFA

    Conductivity

    Direct

    AcidDegassed

    mg/L

    S/cm

    S/cmS/cm

    > 0.2 and < 1.0

    < 1.0

    0.1 - 0.6

    5.5 7.5

    0.9 1.20.2 0.4

    34

    Dose rate: 20 mg/L make-up water

    100 mg/L make-up water (last days)

    DRY LAY-UP WITH FILM FORMING AMINES

    CONDENDATE PARAMETERS WITH CETAMINE

    IN 2012

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    System free of corrosion and deposits (visual inspection) Start-up condensate fully in spec within 5 to 12 hours

    approx. 24 h gain in time

    35

    Start-upcondensate Conductivity[S/cm]

    Acid

    conductivity[S/cm]

    O2[g/L] SiO2

    [g/L] Na[g/L] Fe[g/L] Cu[g/L]

    Specification < 5.0 < 0.3 < 20 < 30 < 20 < 20 < 10

    Measurement

    2012

    2013

    2014 #

    3.89

    6.25

    3.04

    0.29

    0.18

    0.28

    14

    n.d.

    n.d.

    < 5

    < 5

    17

    < 2

    n.d.

    n.d.

    < 2

    < 2

    8

    < 1

    n.d.

    n.d.

    #after 4 h; start-up of turbine delayed by non WSC related issues

    DRY LAY-UP WITH FILM FORMING AMINES

    RESULTS

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    36

    Main feed water tank Raw condensate tank

    COMPLETE STAND-BY PRESERVATION

    DRY LAY-UP WITH FILM FORMING AMINES

    PICTURES OF PLANT INSPECTION 2012

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    37

    Main feed water tank Degasser dome

    DRY LAY-UP WITH FILM FORMING AMINES

    PICTURES OF PLANT INSPECTION 2013

    COMPLETE STAND-BY PRESERVATION

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    Successful dry lay-up of water/steam cycle with film formingamines

    Complete plant protection due to hydrophobic protective film

    Significantly lower iron levels in start-up condensate

    Faster restarts after shut-down periods

    Long lasting film stability under wet and dry conditions

    Highly felxible treatment concept tolerating flexible system

    operation

    No need of dry air or nitrogen

    38

    DRY LAY-UP WITH FILM FORMING AMINES

    CONCLUSIONS

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    39

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    40

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    CONTACT SLIDE

    Andre DE BACHE

    Technical Product Manager Boiler WaterNiederheider Strae 22

    D-40589 Dsseldorf

    Phone + 49 (0)2 11 797 84 10

    Email [email protected]

    Web www.kurita.eu

    mailto:[email protected]://www.kurita.eu/http://www.kurita.eu/http://www.kurita.eu/mailto:[email protected]
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    THANK YOU FOR YOUR ATTENTION

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    www.kurita.eu

    This document is confidential. Any kind of reproduction, change, transfer to a third party or disclosure of this document,

    even extracts, requires the prior written consent of Kurita Europe GmbH.

    http://www.kurita.eu/http://www.kurita.eu/