New Construction of Waste Incineration Plants in Austrian ... · Nov. 15, 2010 New Construction of...
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New Construction of Waste Incineration Plants in Austrian Redevelopment Zones
“Creation of University – Enterprise Cooperation Networks for Education on Sustainable Technologies”
TEMPUS – Meeting
November 15th 2010, Vienna
Gerd Mauschitz
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The lecture gives a short overview about the installation of new waste incineration plants in Austria, especially in zones where a relative high background exposure to air pollutants actually exists.
Especially the high status of clean air technology which is used in Austrian waste incineration plants to mitigate air pollutants will be explained. Without these purification technologies no waste incinerator can set into operation.
Motivation
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in compliance with relevant regulations by law (e.g. ordinance on landfills 2005),
growing waste quantities, especially of bulky refuse, industrial waste, and municipal waste,
rising number of inhabitants,
increasing number of single person households,
decreasing number of local suppliers (grocery stores),
growing number and increasing sales areas of supermarkets,
Arguments for construction of new incineration plants
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sales promotion: “Take 3, pay only for 2!”,
prohibition of agricultural recovery of municipal sewage sludge,
saving of fossil fuels, generating electricity, district and process heat,
mitigation of greenhouse gas emissions,
increasing requirements of lower-cost energy for industry.
Arguments for the construction of new incineration plants
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New waste incineration plants in Austria
Thermal output Capacity
[MW] [twaste/a]
line 2 Jun.06 grate firing 80 225,000
FWW Pfaffenau Pfaffenau 2 lines Sep.08 grate firing 80 250,000
.A.S.A. Zistersdorf Mar.09 grate firing 45 130,000
line 3 Sep.09 grate firing 90 225,000
RHKW (Linz AG) Linz 2011 fluidized bed 66 238,000
Total 361 1,068,000
Combustion technologyCompany Location Remarks Start of
operation
AVN Dürnrohr
WAV (AVE) Wels
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Immission limit values by Austrian Ambient Air Quality Standard (IG-L)
Pollutant HMW MW8 TMW JMW
Suspended particulate matter [µg/m3] - - 150 -
PM10 [µg/m3] - - 50 40 (20)1)
Lead (Pb) on PM10 [µg/m3] - - - 0,5
Nitrogen dioxide [µg/m3] 200 - 801) 30
Sulphur dioxide [µg/m3] 200 - 120 20
Carbon monoxide [mg/m3] - 10 - -
Benzene [µg/m3] - - - 5
1) Target value Legend: HMW half hourly average value; MW8 mean value of eight hours; TMW daily average value; JMW yearly average value
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Minimum number of monitoring points (acc. to IG-L; 2009 in operation)Pollutant Minimum number
of monitoring points 2009 in
operation [%]
SO2 63 116 + 84
NOX 79 153 + 94
CO 27 44 + 63
PM10 77 131 + 70
Lead (Pb) 11 19 + 73
Cadmium (Cd), Arsenic (As), Nickel (Ni) 11 20 + 82
Benzene 12 20 + 67
Benzo-(a)-pyrene 15 19 + 27
Ozone 93 119 + 28
Particulate deposition not defined 164 Pb, Cd on particulate deposition not defined 114
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Number of exceeding of PM10 – limit value (acc. IG-L)
Province Monitoring point TMW -exceedance
max. TMW [µg/m³]
JMW [µg/m³]
Belgradplatz 33 98 26 Stadlau 36 99 27 Liesing 52 84 29
Taborstraße 48 95 29
Vienna
Rinnböckstraße 48 99 30 Linz, Neue Welt 35 124 28 Upper Austria
Linz, Römerbergtunnel 41 181 32 Klosterneuburg 34 102 26 Lower Austria Schwechat 37 87 27
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Number of exceeding of PM10 – limit value (acc. IG-L)Province Monitoring point TMW -
exceedance max. TMW
[µg/m³] JMW
[µg/m³]
Hartberg 32 89 28 Knittelfeld 32 93 27 Köflach 35 109 30
Leibnitz 46 134 30 Peggau 34 113 32 Voitsberg 32 97 29
Graz Don Bosco 76 209 40 Graz Mitte 63 197 36
Graz Nord 37 129 30 Graz Ost 59 146 35
Graz Süd 66 300 36
Styria
Graz West 46 231 30
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Number of exceeding of PM10 – limit value (acc. IG-L)
Province Monitoring point TMW -exceedance
max. TMW [µg/m³]
JMW [µg/m³]
Klagenfurt 42 116 32 St. Andrä 32 101 30
Carinthia
Wolfsberg 42 126 32
Tyrol Innsbruck 46 131 29 Vorarlberg Höchst 32 99 27
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Number of exceeding of PM10 – limit value (acc. IG-L)
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Additional impact for immission situation
maximally 3% of daily average value,
maximally 1% of annually average value.
Irrelevance principle - tolerance criteria
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Capacities and starting dates for three waste incineration plants in Austrian redevelopment zones
Location Capacity Start of operation Redevelopment zone
Wien Pfaffenau 250,000 t/a 2008 PM10, NOX
RHKW Linz 238,000 t/a 2011 PM10, NOX
RVH-Heiligenkreuz 325,000 t/a 2014 ? PM10
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Municipal waste incineration plants in Vienna
Location Realized capacity Start of operation Projected capacity Flötzersteig 200,000 t/a 1963 -
Spittelau 260,000 t/a 1971 260,000 t/a
Pfaffenau 250,000 t/a 2008 450,000 t/a
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Municipal waste incineration plants in Vienna
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Simmering
NGPS Simmering Biomass power station
MWI Pfaffenau
HWI EbS
Biogas power station
Waste water treatment
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Operating parameters of MWI Pfaffenau
MVA Pfaffenau
Quantity of incinerated waste 250,000 t/a Consumption of light fuel oil 250 t/a Thermal capacity 624 GWh
Steam production (vessel) 745,000 t/a Thermal capacity (steam) 544 GWh Electrical capacity (generator) 99 GWhel
Power supply (grid) 68 GWhel Heat supply (district heating grid) 407GWhth
Energetic efficiency 76.12 %
Station supply (electricity) 4 MW Station supply (steam) 10.3 t/h
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Emission limitsfor MWI Pfaffenau
HMW TMW Pollutant / [mg/m3] application official application official
TSP 8 8 - 5 TOC 8 8 - 8 HCl 7 7 - 7 HF 0.3 0.3 - 0.3 SO2 30 20 - 20 NOX 70 70 - 70 CO 100 100 50 50 Hg 0.05 0.05 - 0.05 Mean value 0.5 - 8 hours application official Cd + Tl 0.05 0.05 Heavy metals 0.5 0.5 NH3 5.0 5.0 PAHC - 0.01 Mean value 6 - 8 hours application official Dioxin/Furan 0.1 ng/m3 0.1 ng/m3 PCB - 0.1 ng/m3 B(a)P - 0.1 µg/m3
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Potential of emission substitutionMWI Pfaffenau
[kg/year] Scenario Source/Sink TSP2) NOX SO2 CO Evaluation
A Emissions MWI Pfaffenau1) 1,400 34,000 2,700 31,200 regional
B Substitution: heat supply on heating station
3,200 42,400 26,100 4,000 regional
C Substitution: heat supply on households
31,700 122,700 177,700 1,150,500 regional
D Substitution: electric power supply
500 6,400 4,700 1,700 national
E Regional balance A minus B -1,900 -8,400 -23,400 27,000 regional
F Regional balance A minus C -30,300 -88,700 -175,000 -1,119,300 regional
G National balance A minus B minus D -2,300 -14,800 -28,100 25,500 national
H National balance A minus C minus D -30,800 -95,100 -179,700 -1,121,200 national
1) These values are the mass flows of emissions calculated by using the emission limits which were applied in environmental risk assessment 2) Total suspended particulates
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Process flow sheet of MWI Pfaffenau
Waste hopper
Recovery boiler
Grate firing
Steam turbine
District heating
ElectrostaticPrecipitator
ESP
Waste watertreatment
Grateslag
Scrap Boilerslag
ESPdust
Filtercake
CaSO4 Cleanwater
Activated carbonadsorber
Denoxing(SCR)
Crane Scrubber
SO2+½O2+CaCO3→CaSO4↓+CO2CaO+H2O→Ca(OH)2SO2+½O2+Ca(OH)2→CaSO4↓+H2O
SCR4NO+4NH3+O2→4N2+6H2O6NO2+8NH3→7N2+12H2O
Slag cooler
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Municipal waste incineration plant RHKW Linz
Expected input Mass flow Municipal waste from Linz 100,000 t/a Sewage sludge (30% dry matter) 50,000 t/a
Industrial partners 70,000 t/a
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RHKW Linz
RHKW Linz
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RHKW Linz aerial view
(photomontage)
Stack 180m high
Mechanical waste treatment (MWT) and fuel storage
Conveying equipment for waste from MWT to the waste incinerator
Municipal waste incineration plant
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Emission limits for RHKW LinzHalf hourly mean
value Daily mean value Annually mean value
Concentration of pollutants
Application Official Application Official Application Official
NOX [mg/m³] 70 60 70 55 50 50 CO [mg/m³] 100 100 50 50 50 50 SO2 [mg/m³] 50 40 35 30 20 20 TSP3) [mg/m³] 8 5 5 5 5 4 PM10 [mg/m³] 5 - 5 - 5 - TOC [mg/m³] 8 8 8 8 8 8 HCl [mg/m³] 7 7 7 7 7 7 HF [mg/m³] 0.3 0.3 0.2 0.2 0.2 0.2 Hg [mg/m³] 0.05 0.05 0.05 0.035 0.05 0.02
HMs4) [mg/m³] - - 0.51) - - -
Cd + TI [mg/m³] - - 0.0561) 0.021) - - NH3 [mg/m³] - - 51) 51) - - Dioxine [ng/m3] 0.12) 1) Mean value 0,5 - 8 hours 2) Mean value 6 - 8 hours 3) Total suspended particulates 4) Heavy metals (total)
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Emission limits for RHKW Linz
TSP: HMW, JMW reduced
PM10: HMW, TMW, JMW additionally (acc. AVV)
NOx: HMW, TMW, reduced
Hg: TMW, JMW, reduced
Legend: TSP Total suspended particulatesHMW Half hourly mean valueTMW Daily mean valueJMW Annually mean valueAVV Regulations for waste incineration (BGBl. II Nr. 296/2007)
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NOx – Immission concentration 2007 in Upper Austria and ViennaProvince Monitoring point max.
HMW HMW
>200 µg/m³ JMW
Upper Austria Enns Eckmayermühle 135 0 31 Upper Austria Enns Kristein 190 0 53 Upper Austria Krenglbach 186 0 37 Linz 24er Türme 140 0 33 Linz Neue Welt 148 0 31 Linz Römerbergtunnel 297 11 50 Vienna Belgradplatz 148 0 35 Vienna Floridsdorf 155 0 32 Vienna Gaudenzdorf 163 0 35 Vienna Hietzinger Kai 240 31 71 Vienna Laaer Berg 172 0 31 Vienna Rinnböckstrasse 164 0 45 Vienna Stephansplatz 220 2 32 Vienna Taborstraße 158 0 44 Vienna Währinger Gürtel 133 0 31
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Process flow sheet of RHKW LinzResidues Sewage sludge Electricity and heat generation
District heating
Residues
Combustion air
Bed slag Boiler slag Fine ash CaSO4 Neutralisation sludge
Waste water treatmentCentrifugeCa(OH)2 NH4(OH)
Scrubber Denoxing(SCR)
Fluidez bed incinerator & steam vessel
Adorbent
Water
ESP
CaCO3SiO2
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Regional importance of the location Business Park Heiligenkreuz Heiligenkreuz
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Business ParkHeiligenkreuz
BathSt. GotthardAutomobile Company
Opel
National border
RVHHeiligenkreuz
LenzingFibres
Biomassincinerator
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PM10- Emissions in Burgenland (2007)
Monitoring point EISENSTADT OBERWART KITTSEE Measured value PM10 PM10 PM10
Unit [µg/m³] [µg/m³] [µg/m³] Maximum* 83.3 84.8 66.9
Max. limit value* 50 50 50 Number of exceedings 27 16 13
* Daily mean value (TMW)
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RVH Heiligenkreuz
Expected input Calorific
value [MJ/kg]
Mix 2 [t/a]
Municipal waste 10.9 220,000 Sewage sludge 0.8 70,000 Residues of water treatment, wood, a.o. 11.4 35,000 Total fuels (average incl. sewage sludge) 8.8 325,000 Total thermal capacity 99 MW
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Process flow sheetRVH Heiligenkreuz
Residues
DustSewagesludge Carbon
CaCO3SiO2
Additives
Residues
Combustion air
Electricity and heat generation
Bed slag Metalls
Fluidized bed incinerator&
vessel
SteamElectricity
Condensate
NH4(OH)
Ca(OH)2Acti. C
Boiler slag Fine ash
Water
ESP
Denoxing(SCR)
Adsorber
Met
all r
ecyc
ling
Haz
ardo
usw
aste
depo
sit
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Applied limit values of emission for RVH HeiligenkreuzEU-regulation
2000/76 Waste
incineration
Regulation for waste incineration
AVV, BGBl II 2002/389
RVH Heiligenkreuz projected
TMW* TMW* TMW* HMW*
[mg/m3(Vn)] [mg/m3(Vn)] [mg/m3(Vn)] [mg/m3(Vn)]NOx 200 70 50 70 CO 50 50 50 100 SO2 50 50 35 35 TSP1) 10 10 5 8 TOC2) 10 10 8 8 HCl 10 10 7 10 HF 1 0.5 0.2 0.25 * Related to dry flue gas and 11 Vol.-% O2 1) Total suspended matter 2) Total organic compounds
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MMK Frohnleitenaerial photograph
&photomontage
Thermal capacity: 160 MW; quantity of fired waste: 450,000 t/a
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Waste incineration in Austria (2013)Thermal capacity
Quantity of fired waste
[MW] [twaste/year]MVA Flötzersteig Flötzersteig 3 lines 1963 Grate 50 200,000
MVA Spittelau Spittelau 2 lines 1971 Grate 85 250,000
FWW Pfaffenau Pfaffenau 2 lines Sep.08 Grate 80 250,000
Line 1 + 2 2004 Grate 120 300,000
Line 3 Sep.09 Grate 90 225,000
.A.S.A. Zistersdorf Mar.09 Grate 45 130,000
Line 1 1995 Grate 28.7 75,000
Line 2 Jun.06 Grate 80 225,000
RVL (AVE, Lenzing) Lenzing 2004 Fluidized bed 110 300,000
RHKW (Linz AG) Linz 2011 Fluidized bed 66 238,000
TRV (ENAGES) Niklasdorf Dec.03 Fluidized bed 40 100,000
MMK (Mayr-Melnhof) Frohnleiten 2 lines 2013? Fluidized bed 160 450,000
KRV Arnoldstein Sep.04 Grate 30 80,000
RVH (BEGAS) Heiligenkreuz 2 lines 2012? Fluidized bed 99 325,000
1,083.7 3,148,000
Technology
Total
Name Location Remarks Start of Operation
AVN Dürnrohr
WAV (AVE) Wels
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Résumé Mitigation of emissions must be done using a clean air technology, which shall be always
state of the art.
In any case the application of clean air technology which is state of the art is essential, even if the atmospheric load in the redevelopment zone is more influenced by other emission sources (e.g. traffic).
The implementation of clean air technology must be economically practicable.
Waste heat recovery is a main issue for the selection of process technology and for the selection of plant site, to minimize the immission load in the redevelopment zones.
During the evaluation process of a new project the overall immission inventory must also include the immissions of all other emission sources situated in the redevelopment area.
Limit values of immissions which are regulated by law must be periodically adapted to be always state of the art.
The evaluation of the methods for immission mitigation within the redevelopment zone must be independent on the evaluation of green house gas emissions.
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Thank you for your attention!