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  • Hightech solutions are often based on simple ideasANDRITZ air pollution control

    Energy Community Workshop, October 2012

    Retrofitting of LargeCombustion PlantsCh. Patterer, 31.10.2012, Vienna

  • 2 ANDRITZ Energy & Environment

    Overview of the Andritz Group

    WET Flue Gas Desulphurisation (W-FGD)

    DRY Flue Gas Desulphurisation (D-FGD)

    Comparison of WET and DRY FGD Solutions

    WET and DRY FGD Projects under Execution

    Energy Community WorkshopTable of content

  • 3Company

    ANDRITZ AG, Graz, Austria (Group headquarters)

    More than 180 production and service sites worldwide

    Employees: approximately 17,400 worldwide (as of June 30, 2012)Key figures 2011

    Order intake: 5,707 MEUR

    Sales: 4,596 MEUR

    Net income (including non-controlling interests): 232 MEUR

    Equity ratio (as of end of 2011): 21 %Products and services

    Plants and services for hydropower stations, the pulp and paper industry, solid-liquid separation in the municipal and industrial sectors, the steel industry, and the production of animal feed and biomass pellets

    The ANDRITZ GROUPOverview

    ANDRITZ Energy & Environment

  • 4* Long-term average share of the ANDRITZ GROUPs total order intake

    Electromechani-cal equipment for hydropower plants (mainly tur-bines and genera-tors); pumps; turbo generators

    Systems for the production of all types of pulp and of certain paper grades (tissue, cartonboard); boilers

    Equipment for the mechanical and thermal solid/liquid separation for municipalities and various industries

    Systems for the production and processing of stainless steel and carbon steel strips; industrial furnaces

    Systems for the production ofanimal feed pellets (pet and fish food) and biomass pellets (wood, straw)

    HYDRO40-45%*

    PULP & PAPER30-35%*

    SEPARATION10%*

    METALS10%*

    FEED & BIOFUEL5%*

    ANDRITZ Energy & Environment GmbH company presentation October 2012

    Company ProfileA world market leader in most business areas

  • 5Sales of the ANDRITZ GROUP (MEUR)

    1.110 1.2251.481

    1.744

    2.710

    3.2833.610

    3.1983.554

    4.596

    2002 2003 2004 2005 2006 2007 2008 2009 2010 2011

    PULP & PAPER1990 Sprout-Bauer1992 Durametal1994 Kone Wood1998 Kvaerner Hymac1999 Winberg2000 Ahlstrom Machinery2000 Lamb Baling Line2000 Voith Andritz Tissue LLC (JV)2002 ABB Drying2003 IDEAS Simulation 2003 Acutest Oy2003 Fiedler2004 EMS (JV)2005 Cybermetrics2005 Universal Dynamics Group2006 Ksters2006 Carbona2006 Pilo2007 Bachofen + Meier2007 Sindus2008 Kufferath2009 Rollteck2010 Rieter Perfojet2010 DMT/Biax2011 AE&E Austria2011 Iggesund Tools2011 Tristar Industries2011 Asselin-Thibeau

    FEED & BIOFUEL1995 Jesma-Matador2000 UMT2005 Chemes Strojarne

    HYDRO2006 VA TECH HYDRO2007 Tigp2008 GE Hydro business2008 GEHI (JV)2010 Precision Machine2010 Hammerfest Strm (55.4%)2010 Ritz2011 Hemicycle Controls

    SEPARATION1992 TCW Engineering1996 Guinard2002 3SYS2004 Bird Machine2004 NETZSCH Filtration2004 Fluid Bed Systems of

    VA TECH WABAG2005 Lenser Filtration2006 CONTEC Decanter2009 Delkor Capital Equipment2009 Frautech2010 KMPT

    METALS1997 Sundwig1998 Thermtec2000 Kohler2002 SELAS SAS Furnace Div.2004 Kaiser2005 Lynson2008 Maerz2012 Bricmont2012 Soutec

    Strengthening of the Market PositionGrowth through organic expansion and acquisitions

    ANDRITZ Energy & Environment

  • 6Important Key Figures Q2 and H1 2012 at a GlanceSatisfactory business development

    Unit H1 2012 H1 2011 +/- Q2 2012 Q2 2011 +/- 2011

    Order intake MEUR 2,554.4 3,644.5 -29.9% 1,193.2 1,978.5 -39.7% 5,706.9

    Order backlog (as of end of period) MEUR 6,935.9 7,249.0 -4.3% 6,935.9 7,249.0 -4.3% 6,683.1

    Sales MEUR 2,437.8 2,011.1 +21.2% 1,252.1 1,087.4 +15.1% 4,596.0

    EBITDA MEUR 184.7 157.0 +17.6% 98.2 88.3 +11.2% 386.2

    EBITA MEUR 155.6 131.6 +18.2% 83.1 75.5 +10.1% 331.5

    EBIT MEUR 143.1 123.1 +16.2% 76.4 71.1 +7.5% 312.7

    EBT MEUR 149.8 127.1 +17.9% 79.7 72.1 +10.5% 321.7

    Financial result MEUR 6.7 4.0 +67.5% 3.3 1.0 +230.0% 9.0

    Net income (including non-controlling interests) MEUR 107.5 89.7 +19.8% 57.1 50.9 +12.2% 231.5

    Cash flow from operating activities MEUR 119.4 206.8 -42.3% 88.2 55.7 +58.3% 433.8

    Capital expenditure MEUR 34.5 23.5 +46.8% 15.0 13.2 +13.6% 77.0

    EBITDA margin % 7.6 7.8 - 7.8 8.1 - 8.4

    EBITA margin % 6.4 6.5 - 6.6 6.9 - 7.2

    EBIT margin % 5.9 6.1 - 6.1 6.5 - 6.8

    Employees (as of end of period) - 17,420 16,119 +8.1% 17,420 16,119 +8.1% 16,750

    ANDRITZ Energy & Environment

  • 7Broad research coverageBaader Bank, Berenberg Bank, Cheuvreux, Commerzbank, Deutsche Bank, Erste Bank, Goldman Sachs, Hauck & Aufhuser, HSBC, J.P. Morgan, Kepler Capital Markets, RCB, UBS

    Relative share price performance of the ANDRITZ share versus the ATX since the IPO:

    Performance June 2001(ANDRITZ IPO) untilJune 30, 2012: ANDRITZ: +1,444% ATX: +60%

    Performance in H1 2012: ANDRITZ: +23% ATX: -2%

    Market capitalizationANDRITZ as ofJune 30, 2012: 4,215 MEUR

    Note: On April 23, 2012, the ANDRITZ share was split in a ratio of 1:2. All share price data and key figures were adjusted accordingly.1 June 2001: IPO at 2.63 EUR/share 2 June 2003: Secondary Public Offering at 2.85 EUR/share 3 Closing price as of March 30, 2012: 40.52 EUR

    ANDRITZ ShareSolid performance, broad research coverage

    ANDRITZ Energy & Environment

  • 8Pulp & Paper

    ServicesPaper

    TechnologyMechanical

    PulpingFiber

    PreparationPulp DryingRecovery &

    PowerFiber and Chemical

    Wood Processing

    ANDRITZ GROUP

    Air Pollution Control

    Steam generators and plants

    ANDRITZ Energy & Environment

    Power plant services

    Air Pollution Control within ANDRITZDiversified product range and a clear focus

  • WET Flue Gas Desulphurisation (W-FGD)Limestone based open spray tower technology

  • 10

    Raw gas

    Cleangas

    Gypsum

    Limestonepowder

    Process characteristics: Open spray tower optimized by advanced CFD tools Removing of acid gaseous pollutants (SO2, HCl, HF) Low operation cost due to low sorbent costs (limestone) Low maintenance costs Beneficial use for solid product (marketable gypsum) Most used technology worldwide

    Performance data: High SO2 removal rate: up to 99 % SO3 removal rate: up to 70 % Dust removal rate: up to 80 % High HCl removal rate: up to 99 %

    Capacity: Flue gas volume flow: 4.8 Mio. m3/h (std,wet) SO2 concentration: up to 30,000 mg/m3 (std,dry)

    Applications: Power stations (bituminous coal, lignite, fuel oil, ..) Industry (cement, steel, ..)

    WET Limestone Flue Gas DesulphurizationWell proven technology for high removal efficiencies

    ANDRITZ Energy & Environment

  • 11

    Advantages:

    Low operation cost

    Low maintenance costs

    Limestone as available and cheap absorbent

    Producing marketable gypsum

    WET Limestone Flue Gas DesulphurizationTailor made solutions for each application

    ANDRITZ Energy & Environment

  • 12

    Removing of acidic gaseouspollutants (SOX, HCl, HF) anddust

    ANDRITZ Energy & Environment

    Clean gas

    Gypsum

    Limestone

    Water

    Oxidation air

    Raw gas

    WET Limestone Flue Gas DesulphurizationOne process step for various pollutants

  • 13 ANDRITZ Energy & Environment

    WET Limestone FGD Process and Auxiliary SystemsHighly efficient and maintenance friendly

    Limestone Storage, Slurry Preparation System

    Gypsum Dewatering and Storage System

    Absorber, Oxidation Air System, Slurry Recirculation

    Waste Water Discharge

    Ash Removal System

  • 14

    FGDplus as Enhancement of the Open Spray TowerReduced investment as well as operation costs

    Process characteristics: Scrubber with adapted mass-transfer regime Optimized combination of high removal and fine removal

    within the absorption zone Increase SO2-removal efficiency for high inlet concentration Maximize dust, aerosol and HM removal Decrease of invest costs

    Number of spray banksAbsorber height (sump, absorption zone)Pump size

    Decrease of operation costs Pressure at nozzlesDecrease of liquid to gas ratioOptimized behavior at variable load conditions

    Capacity: Flue gas volume: up to 4.8 Mio. m3/h (std,wet) SO2 concentration: up to 30,000 mg/m3 (std,dry)

    Applications: Upgrade of existing absorber New installations

    Liquid Bulk

    Raw Gas

    Redispersed Droplets

    Velocity magnitude (regions only) [m/s]

    ANDRITZ Energy & Environment

  • 15 ANDRITZ Energy & Environment

    Ca(OH)2 + SO2 = CaSO3 * H2O + H2O (1)

    Ca(OH)2 + SO3 = CaSO4 * H2O + H2O (2)

    Ca(OH)2 + SO2 + O2 = CaSO4 * H2O + H2O (3)

    CaSO3 * H2O + O2 = CaSO4 * H2O (4)

    Ca(OH)2 + CO2 = CaCO3 + H2O (5)

    Ca(OH)2 + 2 HCl = CaCl2 * 2 H2O (6)

    Ca(OH)2 + 2 HF = CaF2 + 2 H2O (7)

    Wet FGD Process Product Sorbent

    Basic Wet Flue Gas Cleaning ChemistryOverall chemical reactions

  • 16 ANDRITZ Energy & Environment

    Basic Sorbent Requirements for Wet Flue Gas CleaningSorbent quality significantly impacts the system efficiency

    Limestone Unit minimum preferredCaCO3 [wt. %] > 90 > 95

    MgCO3 *) [wt. %] < 4.0 < 2.0

    Inerts [wt. %] < 6.0 < 3.0

    Grain size distribution d90 (powder) [m] < 63 90 < 44 63

    Grain size (pebbles)**) [mm] < 80

    Reactivity - according to Andritz standard reactivity testAverage middle European price [/to] ~ 35 55*) Considered as soluble and reactive**) In case of onsite crushing and milling plant

  • 17 ANDRITZ Energy & Environment

    Basic Wet Flue Gas Cleaning Performance FiguresHigh removal efficiencies for various trace components

    Removed trace component Unit normal maximumSulphur dioxide SO2 [%] 90 - 97 ~ 99

    Sulphur trioxide SO3 [%] 50 - 60 ~ 70

    Hydrochloride HCl [%] 90 - 97 ~ 99

    Hydrofluoride HF [%] 95 - 97 ~ 99

    Particulate matter [%] 50 - 75 ~ 80

    Mercury *) Hg [%] 75 - 80 ~ 95

    Heavy metals **) [%] Mainly accomplished by pre wet FGD dust removal*) for oxidized Mercury**) Sb, As, Pb, Cr, Co, Cu, Mn, Ni, V, Sn

  • DRY Flue Gas Desulphurization (D-FGD)Circulating dry scrubbing (CDS)

  • DRY Flue Gas Cleaning Based on CFB TechnologyBasic process characteristics

    ANDRITZ Energy & Environment 19

  • DRY Flue Gas Cleaning Based on CFB TechnologyNo moving parts in the flue gas path

    Circulating fluidized bed with intense and turbulent contact between solid sorbent and flue gas

    Water injection for re-activation of absorbent

    CFD optimized turboreactor inlet including venturi nozzle(s)

    Filter designed for very high solids amounts

    Cleangas

    Raw gasfrom boiler

    WaterHydrated lime

    Product recirculation and discharge

    ANDRITZ Energy & Environment 20

  • 21

    Process characteristics: Dry flue gas cleaning optimized by advanced CFD tools Dry flue gas cleaning is based on fluidized bed technology Removing of acid gaseous pollutants (SO2, HCl, HF) Low investment costs Applicable for installation up to 600 MWel

    Performance data: High SO2 removal rate: up to 99 % High SO3 removal rate: up to 99 % High dust removal rate: up to 99.99 % High HCl removal rate: up to 99 %

    Capacity: Flue gas volume flow: 50,000 to 1.2 Mio. m3/h (std, wet) SO2 inlet concentration: up to 20,000 mg/m3 (std, dry)

    Application: Small to middle sized power stations Industry (cement, steel, ..), EfW and biomass plants

    Cleangas

    Raw gasfrom boiler

    FGD product(for disposal mainly)

    WaterHydrated

    Lime

    DRY Flue Gas Cleaning Based on CFB TechnologySingle step process for high removal efficiencies

    ANDRITZ Energy & Environment

  • 22 ANDRITZ Energy & Environment

    CDS Process and Auxiliary SystemsA simple system for high performance

    Sorbent System

    Product Discharge System

    Turboreactor, Baghouse Filter, Product Recirculation System

    Process Water

  • 23 ANDRITZ Energy & Environment

    Ca(OH)2 + SO2 = CaSO3 * H2O + H2O (1)

    Ca(OH)2 + SO3 = CaSO4 * H2O + H2O (2)

    Ca(OH)2 + SO2 + O2 = CaSO4 * H2O + H2O (3)

    CaSO3 * H2O + O2 = CaSO4 * H2O (4)

    Ca(OH)2 + CO2 = CaCO3 + H2O (5)

    Ca(OH)2 + 2 HCl = CaCl2 * 2 H2O (6)

    Ca(OH)2 + 2 HF = CaF2 + 2 H2O (7)

    Dry FGD Process Product Sorbent

    Basic Dry Flue Gas Cleaning ChemistryOverall chemical reactions

  • 24 ANDRITZ Energy & Environment

    Basic Sorbent Requirements for Dry Flue Gas CleaningSorbent quality significantly impacts the system efficiency

    Hydrated lime Ca(OH)2 Unit minimum preferredContent of free, reactive Ca(OH)2 [wt. %] > 80 > 90

    Moisture [wt. %] < 2 < 1

    Specific surface (BET-method) [m2/g] > 15 > 18

    Grain size distribution d50 [m] < 8 < 5

    Average middle European price [/to] ~ 150 180

    Burnt lime CaO*) Unit minimum preferredContent of free, reactive CaOnot sintered, soft burnt [wt. %] > 85 > 90

    Rest CO2 [wt. %] < 5 < 3

    t60 value [min] < 4 < 2

    Mean particle diameter d50 [mm] < 2 < 0,2

    Average middle European price [/to] ~ 70 100*) In case of onsite hydration plant

  • 25 ANDRITZ Energy & Environment

    Basic Dry Flue Gas Cleaning Performance FiguresHigh removal efficiencies for various trace components

    Removed trace component Unit normal maximumSulphur dioxide SO2 [%] 90 - 95 ~ 99

    Sulphur trioxide SO3 [%] 95 - 98 ~ 99

    Hydrochloride HCl [%] 90 - 97 ~ 99

    Hydrofluoride HF [%] 95 - 97 ~ 99

    Particulate matter [%] 99.9 99.95 ~ 99.99

    Mercury Hg [%] 90 - 95 ~ 97

    Heavy metals *) [%] 95 98 ~ 99*) Sb, As, Pb, Cr, Co, Cu, Mn, Ni, V, Sn

  • 26 ANDRITZ Energy & Environment

    Basic Dry Flue Gas Cleaning ArrangementCompact layout and small footprint

  • 27 ANDRITZ Energy & Environment

    Basic Dry Flue Gas Cleaning ArrangementCompact layout and small footprint for 2 x 145 MWel

  • 28 ANDRITZ Energy & Environment

    Basic Dry Flue Gas Cleaning ArrangementRevised design reduces investment costs significantly

  • 29 ANDRITZ Energy & Environment

    Dry Flue Gas Cleaning in OperationA view into the Turboreactor beneath the venturi nozzles

  • WET or DRY Flue Gas Desulphurisation SolutionsA comparison of two well proven technologies

  • 31 ANDRITZ Energy & Environment

    About 85 to 90 % of installed FGDs worldwide are based on wet technology. The reasons are mainly lower operational cost (cheap limestone can be used, dry FGDs operate with more expensive burnt lime) and the production of commercial grade gypsum.

    However, there are also arguments for dry FGD. For certain applications and for smaller power stations dry FGD might be the better solution. Which are the selection criteria to choose the right system?

    Wet FGD

    Dry FGD

    Wet FGD versus Dry FGDOperation costs versus investment costs

  • 32 ANDRITZ Energy & Environment

    Selection Criteria WET versus DRY FGD (1 of 3)Sorbent costs and basic design parameters

    Parameter WET FGD DRY FGD RemarkFlue gas volume 100,000 4,800,000

    m3/h (std, wet)50,000 1,200,000

    m3/h (std, wet)

    Installed boiler capacity

    ~ 1,100 MWel ~ 150 MWel (lignite)~ 300 MWel (hard coal)

    Capacity just for information, flue gas volume is decisive

    SO2 removal efficiency > 99 % up to 99 % (95 %)

    Sorbent consumption CaCO3 (limestone)SF 1.03

    CaO / Ca(OH)2SF 1.3 1,8 (depending on removal efficiency)

    Yearly operating hours to be considered

    Sorbent costs(middle European) 35 /to 70 /to

    Water consumption 100 % 80 %

    Possible dust inlet concentration

    < 200 mg/m3 (std, dry) Dust removal in wet

    FGD limited

    < 125 g/m3 (std, dry) High dust removal in

    dry FGD

    Dry FGD may be interesting for retrofit (ESP performance in old plants)

  • 33 ANDRITZ Energy & Environment

    Selection Criteria WET versus DRY FGD (2 of 3)Beneficial product use and waste discharge

    Parameter WET FGD DRY FGD RemarkSO3 removal < 50 % > 99 % Important for oil fired

    boilers

    FGD product Commercial grade gypsum

    OR disposal gypsum

    Product for disposal (CaSO3/CaSO4)

    Is beneficial product use required?What are the disposal costs?

    Waste water If commercial grade gypsum is produced, waste water has to be

    discharged

    Waste water free system

    Can waste water be discharged?What kind of waste water treatment is required?

    Maintenance cost higher lower

    Erection period ~ 30 Mo ~ 24 Mo

    Power consumption /pressure drop

    Lower pressure drop especially for part load

    Lower power consumption for

    auxiliary equipment

    Has to checked on a case by case basis

  • 34 ANDRITZ Energy & Environment

    Selection Criteria WET versus DRY FGD (3 of 3)Boundary conditions for retrofit projects

    Parameter WET FGD DRY FGD RemarkCondition of existing stack

    Existing stack has to be modified in all

    cases long outage of boiler

    Existing stack can most of the times be used without modification

    Stack condition has to checked in case of dry FGD application

    Boiler ID fan Lower pressure drop possible that

    existing ID fan can be modified and used

    Operation flexibility 20 100 % 20 100 % Flue gas recirculation < 60 % is necessary for dry FGD applications

    Flue gas temperature at FGD outlet

    Saturation temperature50 60 C

    75 85 C Required stack outlet temperature has to be checked

  • 35 ANDRITZ Energy & Environment

    WET versus DRY FGD Case Study 1 (Lignite)660 MWel, 11,000 mg/m3 (std, dry) 2.8 Mio. m3/h (std, wet)

    Parameter WET FGD DRY FGD RemarkSorbent consumption 48 to/h 50 to/h

    Sorbent costs per year (7,000 operating hours)

    ~ 11.8 Mio. 24.5 Mio. 12.7 Mio. higher sorbent costs per year for dry FGD

    Equipment 1 wet scrubber 3 dry scrubbers

    Water consumption

    Electrical power consumption

    Invest costs*) Emission limit: 200 mg/m (std, dry)

    Based on usual boundary conditions and requirements only a wet FGD installation is

    financially reasonable

  • 36 ANDRITZ Energy & Environment

    WET versus DRY FGD Case Study 2 (Hard Coal)200 MWel, 3,500 mg/m3 (std, dry) 0.7 Mio. m3/h (std, wet)

    Parameter WET FGD DRY FGD RemarkSorbent consumption 3.9 to/h 3.4 to/h

    Sorbent costs per year (6,000 operating hours)

    ~ 0.82 Mio. 1.43 Mio. 0.61 Mio. higher sorbent costs per year for dry FGD

    Equipment 1 wet scrubber 1 dry scrubber

    Water consumption 38 m3/h 28 m3/h Less with dry FGD

    Electrical power consumption

    ~ 2,000 kWh/h ~ 1,500 kWh/h Less with dry FGD

    Amount of FGD product

    8.0 to/hGypsum

    6.0 to/hLandfill

    Landfill costs have to be evaluated

    Waste water discharge 1.5 m3/h - Dry FGD can be used as waste water sink

    Invest costs 100 % 70 %*) Emission limit: 200 mg/m (std, dry)

  • The Andritz Turbo-CDS technology has been installed in 21 coal fired power plants (35 turboreactor trains) in Europe, China and USA with a total capacity of > 2,000 MWel.

    Due to numerous advantages in comparison to wet FGD and semi-dry spray absorption the CDS based technology has gained a considerable share in the flue gas cleaning market

    Most important is the possibility to remove nearly all pollutants apart from CO and NOx in one process step

    The CDS technology is waste water free and can be used as waste water sink

    Single vessel units for boiler sizes up to 300 MWel are state of the art

    Executive SummaryThe market share of CDS based FGD systems will increase

    37 ANDRITZ Energy & Environment

  • Projects under executionANDRITZ air pollution control

  • Technical data:

    Fuel: Hard coal

    Capacity: 1 x 910 MWel

    Flue gas volume: 2,500,000 m/h (std,wet)

    SO2 inlet: 3,800 mg/m (std,dry)

    Removal efficiency: > 95%

    Customer: EnBW Start Up: 2012

    Karlsruhe, Germany

    Wet limestone FGD

    Technology/Supply:ESP, ash handling system, flue gas system, absorber, limestone slurry supply, gypsum dewatering and storage, installation & commissioning

    39 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: Hard coal

    Capacity: 800 MWel

    Flue gas volume: 2,000,000 m/h (std,wet)

    SO2 inlet: 1,300 mg/m (std,dry)

    Removal efficiency: 95.0%

    Customer: Trianel Start Up: 2012, Consortium: SIEMENS / IHI / AE&E

    Lnen, Germany

    Wet limestone FGD

    Technology/Supply:Civil engineering, absorber, ducts, limestone slurry supply, gypsum dewatering and storage, booster fan, waste water treatment plant, installation &commissioning

    40 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: Lignite

    Capacity: 4 x 330 MWel

    Flue gas volume: 2,800,000 m/h (std,wet)

    SO2 inlet: 5,630 mg/m (std,dry)

    Removal efficiency: 96.4%

    Customer: SC Complexul Energetic,Turceni SAStart Up: 2012

    Turceni, Romania

    Wet limestone FGD

    Technology/Supply:Turnkey plant, 4 absorbers, flue gas system incl. flue gas fans, limestone slurry preparation plant, gypsum dewatering and storage, installation & commissioning

    41 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: Lignite

    Capacity: 1 x 660 MWel

    Flue gas volume: 2,517,800 m/h (std,wet)

    SO2 inlet: 5,630 mg/m (std,dry)

    Removal efficiency: > 96%

    Customer: CEZ a.s.Start Up: 2013

    Ledvice, Czech Republic

    Wet limestone FGD

    Technology/Supply:Civil works, absorber, ducts, limestone storage and slurry system, gypsum dewatering system, installation & commissioning Turnkey project

    42 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: lignite

    Capacity: 3 x 250 MWel

    Flue gas volume: 3 x 1,010,800 m/h (std,wet)

    SO2 inlet: 11,197 mg/m (std,dry)

    Removal efficiency: 89,2%

    Customer: CEZ a.s., Skoda Praha InvestStart Up: 2014

    Prunerov, Czech Republic

    Wet limestone FGD

    Technology/Supply:Turnkey wet FGD plant, 3 absorbers, auxiliary systems

    43 ANDRITZ Energy & Environment

  • Technical data:Fuel: Mixed petroleum residue

    Capacity: 820 MWth(5 existing, 2 new boilers)

    Flue gas volume: 2 x 505,000 m/h (std,wet)

    SO2 inlet: 2,600 mg/m (std,dry)

    Removal efficiency: 93.1%

    Dust outlet: 20 mg/m (std,dry)

    Customer: MOL, Slovnaft a.s Start Up: 2011

    Slovnaft, Slovak Republic

    Wet limestone FGD

    Technology/Supply:Turnkey FGD plant after refinery power plant, 2 absorbers, steam reheater, limestone preparation, gypsum dewatering, 2 gypsum silos

    44 ANDRITZ Energy & Environment

  • Technical data:Fuel: Waste water sludge

    Flue gas volume: 2 x 80,000 m/h (std,wet)

    Hg inlet: 0.3 mg/m (std,dry)

    Hg outlet: 0.03 mg/m (std,dry)

    PCDD/PCDF inlet: 12 ngTE/m (std,dry)

    Sorbent: Activated carbon

    Customer: BASFStart Up: 2012

    Ludwigshafen, Germany

    Dry sorption

    45 ANDRITZ Energy & Environment

  • Technical data:Fuel: Lignite

    Capacity: 2 x 145 MWel

    Sulfur content: up to 3.5%

    Flue gas volume: 2 x 610,000 m/h (std,wet)

    SO2 inlet: up to 15,000 mg/m (std,dry) 1,100 mg/m (std,dry) to TS

    SO2 in clean gas: < 200 mg/m (std,dry)

    SO2 removal: > 80 % in TS plant> 98.5 % total

    Sorbent: CaO and fly ash from CFB boiler

    Customer: Adularaja EnerjiStart Up: 2013, Installed after CFB boiler without pre-dedusting

    Yunus Emre, Turkey

    Dry FGD (Turbo CDS with ESP)

    46 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: coal

    Capacity: 150 MWel

    Flue gas volume: 650,000 m/h (std,wet)

    SO2 inlet: 2,600 mg/m (std,dry)

    Removal efficiency: 93.1%

    Dust outlet: 20 mg/m (std,dry)

    Customer: Community Timisoara Start Up: 2013

    Timisoara, Romania

    Dry FGD (Turbo-CDS)

    Technology/Supply:Turnkey Turbo CDS plant after coal-fired CFB boiler,CDS-reactor, fabric filter, absorbent storage andpreparation, product handling and storage.

    47 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: coal

    Capacity: 2 x 140 MWel

    Flue gas volume: 2 x 600,000 m/h (std,wet)

    SO2 inlet: 2,000 mg/m (std,dry)

    Removal efficiency: 80 %

    Dust outlet: 45 mg/m (std,dry)

    Customer: AES Start Up: 2013, 2014

    Tocopilla, Chile

    Dry FGD (Turbo CDS)

    Technology/Supply:Turnkey Turbo CDS plant after coal-fired power plant, 2 reactors, fabric filters, absorbent storage and preparation, product handling and storage, desalination plant

    48 ANDRITZ Energy & Environment

  • Technical data:

    Fuel: coal

    Capacity: 1 x 120 MWel, 1 x 220 MWel

    Flue gas volume: 1 x 550,000 m/h (std,wet)

    1 x 910,000 m/h (std,wet)

    SO2 inlet: 2,000 mg/m (std,dry)

    Removal efficiency: 80 %

    Dust outlet: 15 mg/m (std,dry)

    Customer: AES Start Up: 2013, 2014

    Ventanas, Chile

    Dry FGD (Turbo CDS)

    Technology/Supply:Turnkey Turbo-CDS plant after coal fired power plant, 1 reactor, fabric filters, absorbent storage and preparation, product handling and storage, desalination plant

    49 ANDRITZ Energy & Environment

  • Waagner-Biro-Platz 18074 Raaba, Austria Phone: +43 (316) 501 0Fax: +43 (316) 501 [email protected] www.andritz.com/aee

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    51 Flue Gas Cleaning Expert Conference 2011, ANDRITZ Energy & Environment