Meeting New Environment Norms - Challenges and Possibilities. Presented by: A.K.Sinha General Manager NTPC Limited

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Meeting New Environment Norms - Challenges and Possibilities Presented by: A.K.Sinha General Manager NTPC Limited email: aksinha01@ntpc.co.in

Old v/s New Environment Norms NEW NORMS (mg/nm3) OLD NORMS Installed before 31.12.2003 Installed after 01.01.2003 & To be installed upto 31.12.2016 from 01.01.2017 Unit Size All < 500 MW > 500 MW < 500 MW > 500 MW All SO2 Dispersion through Chimney 600 200 600 200 100 NOx No Standard 600 300 100 SPM 100 100 50 30 Mercury No Standard 0.03 0.03 x 0.03 2

Available Technology Options for Emission Control 3

DeNOx Technologies Available Technology In Combustion Combustion Modification Variants & Low NOx Burner, measures to control Windbox modification, NOx Various type of over fire air Post Combustion Selective Non Catalytic Selective Catalytic erduction (SNCR) Reduction (SCR) Reagent: Catalyst type: Anhydrous/Aqueous Plate/ Honeycomb Ammonia OR Urea Reagent: Anhydrous/ Aqueous Ammonia or Urea 25-40 % 90 % & Above Reduction Efficiency Installation Cost 20 60 % Low Moderate High Operational Cost None High (manly reagent cost) Staging of combustion air Using NH3 4NO + 4NH3 +O2 4N2 + 6H2O Using Urea 4NO + 2CO(NH2)2 + O2 4N2 + 4H2O +2CO2 870 to 1100 C High (Aux power, reagent cost & catalyst replacement) 4NO + 4NH3 +O2 4N2 + 6H2O 2NO2 + 4NH3 + O2 3N2 + 6H2O Process of NOx reduction Temperature required NA 300 to 400 C 4

DeNOx Technologies Combustion Modification Selective Non-Catalytic Reduction (SNCR) Selective Catalytic Reduction (SCR) 5

Performance of DeNOx Technologies 6

Catalyst Type Plate Type Catalyst Honeycomb catalyst

Ash Accumulation over SCR Catalyst - a major challenge in O&M 8

SCR Catalyst Deactivation Poisoning by chemical attack (Arsenic, Phosphorus, Heavy Metals) Masking of catalyst surface by ash Plugging of catalyst surface pores by fine ash particles Sintering causing alteration of catalyst pore structure (due to exposure to high temperatures beyond 450OC 9

SCR Catalyst Erosion High ash Erosive Content of Ash (Silica + Alumina, typically > 85% for Indian coal ash) Ash particle size and shape Plugging susceptibility of catalyst 10

NH3 High Dust SCR BLR A P H SCR ESP FGD STACK Possible SCR Configuration to deal with high ash Lowest Dust, Cold End SCR BLR ESP A P H A P H SCR ESP FGD FGD GGH STACK Low Dust SCR, Hot ESP BLR STACK NH3 DUCT BURNER NH3 Low Dust SCR BLR CS SCR A P H ESP FGD STACK SCR NH3

DeNOx Technologies Challenges DeNOx technology is yet to be established for high and erosive ash coals Technology proven only upto dust load of 30-40 gm/nm3 against our requirement of 80-90 gm/nm3 SCR catalyst is and extremely fast moving highly expensive item (life expectancy 1.5-2 yrs) Very limited SCR catalyst suppliers worldwide, none in India Way Forward A cautious approach needs to be adopted rather than embarking upon hurriedly Pilot slip stream tests with India coals will provide quick learning opportunity both to the manufacturers as well as the plant operators Cyclone dust separators upstream of SCR could be a good approach to start with Rapid indigenization of catalyst manufacturing a must for long term sustenance 12

DeSOx Technologies 13

DeSOx Technologies Parameters WET Limestone FGD DRY FGD (SDA/CDS/NID) Commercially Available Range ~ 1,100 MWe ~ 300-400 MWe single absorber.. For NID each module of 75 MWe SO2 removal efficiency Upto 99 % up to 99 % (90-95 % for SDA) Installation Cost (ZLD & High Chimney lining cost incl.) Operating Cost Moderate Low Sorbent Sorbent costs (Rs/ton) Water consumption CaCO3 (limestone) ~ 2000 1.0 with GGH 1.4without GGH CaO / Ca(OH)2 ~ 6000 0.7 Auxiliary Power Consumption Flue gas temperature at FGD outlet High with GGH Moderate without GGH Saturation temperature 50 60 C (Without GGH) Moderate SO3 removal < 40 % > 98 % Condition of existing stack Existing stack to be modified in Existing stack can be used without all cases modification High 75 85 C

DeSOx Technologies Parameter WET Limestone FGD DRY FGD (SDA/CDS/NID) FGD by-product disposal Gypsum is produced which is saleable when limestone purity is > 90%. & emission from ESP < 50 mg/nm3 Waste water generated which needs to be treated for Zero liquid discharge (ZLD) ~ 30 Months Product for disposal (CaSO3/CaSO4). Space required for disposal Waste water Erection period Waste water free system and can also utilise waste water from other sources. ~ 24 Months 15

DeSOx Technologies Wet Limestone Slurry Scrubbing (WFGD) 70-80% of FGDs worldwide are Wet Limestone FGD

DeSOx Technologies Sea Water FGD Preferred option for Coastal Plants 17

DeSOx Technologies Spray Dryer Absorber (SDA) SO2 + CaO + 1/2 H2O CaSO / H2O CaSO3 + ½O2 + 2H2O CaSO H O SDA is the second most popular FGD technology after Wet Limestone FGD

DeSOx Technologies Circulating Dry Scrubber

DeSOx Technologies Novel Integrated Desulfurization (NID) 20

DeSOx Technologies Regenerative Activated Coke Technology (ReACT) 21

Limestone Factsheet Production of limestone in India was 278.7 million tonnes during 2013-14 There were 23 public and 694 private sector mines during 2013-14 The share in production of public sector mines was 4.2% in 2013-14. Cement companies account for 50% of limestone production and mostly have their own captive mines. Majority of limestone is of 80%-85% purity which will produce gypsum for cement or fertiliser consumption. Current Gypsum rates vary between 700-1200 per Ton. High quality limestone mostly available in Rajasthan Limestone mines are distributed almost all over India. 22

DeSOx Technologies Challenges Wet DeSOx technologies are relatively more matured yet new to majority of Indian operators Wet limestone based FGD, although a preferred option, has large consumptive water requirement associated with extremely polluted blow down which must be taken care through an expensive ZLD system Lime stone supply and gypsum off take chain needs to be evolved quickly FGD retrofit may not be possible in many of the older stations Way Forward No major issues in adoption in new units

Chimney Material for Retrofit Cases ITEM BOROSILICATE GLASS BLOCKS GLASS FLAKE REINFORCED VINYL ESTER COATING 51 MM 1.5 MM UPTO 199 DEG C CONTONUOUS UPTO 140 DEG C CONTINUOUS DESIGN LIFE 30 YEARS 8-10 YEARS GUARANTEE LIFE 10 YEARS 3-4 YEARS VERY HIGH LOW HADEK, NETHERLANDS AKZONOBEL, JOTUN, DENSO, CORROCOAT, HEMPEL, STEULLER THICKNESS SERVICE TEMPERATURE COST SUPPLIERS ECOCERA, KOREA APPLICATOR EXECUTION TIME LOCAL APPLICATOR TRAINED BY SUPPLIER AUTHORIZED APPLICATORS 2-3 MONTHS 2-3 MONTHS 24

Chimney Material for New Builds ITEM FRP FLUE LINER Titanium Clad Sheet 25MM 1.2 MM Ti+ 10 MM MS UPTO 150 DEG C CONTONUOUS UPTO 900 DEG C CONTONUOUS DESIGN LIFE 30 YEARS 20 YEARS GUARANTEE LIFE 3 YEARS - LOW HIGH PLASTICON, DENMARK CHINESE SUPPLIERS THICKNESS SERVICE TEMPERATURE COST SUPPLIERS FIBROGRATS, INDORE APPLICATOR EXECUTION TIME AUTHORIZED APPLICATORS FABRICATION IS COMPLEX. DATA NOT AVAILABLE 6-8 MONTHS 6-* MONTHS 25

Borosilicate Glass FRP Flue Liner Flake Glass Coating 26

Mercury Emission Control Globally, there is no mature / commercially available technology for mercury emission control Fortunately, India coals have relatively lower mercury content (0.5 ppm) The other emission control measures like FGD and ESP by default capture a significant portion of mercury 27

Closed Cycle Cooling - Implications Inland Project Retrofits Higher consumptive water requirement due to higher evaporation losses Reduced power generation efficiency due to higher cooling water temperature by around 2%. Serious layout constraints within acquired land limits Coastal Projects Coastal projects are endowed with abundance of saline sea water and should be permitted to employ open cycle cooling for better efficiency (lower emissions) Sea water FGD is the least cost option for desox which will be completely ruled out if open cycle cooling is not permitted

Reduced Water Consumption (2.5m3/Hr/MW) Typically 2.1m3/Hr/MW of water is lost in closed cycle cooling from the cooling towers Limestone based wet FGD consumes about 0.25 m3/hr/mw of water In addition, there are evaporation and seepage losses from bottom ash dyke Hardly any water left for other consumptive needs DM water consumption Potable water Fugitive coal and ash dust suppression Green belt and plant horticulture 29

Conclusion Promulgation of new environment norms by MoEF is a commendable move The emission norms are comparable with the best in the world However, in order to make implementation of the norms more practicable and better feasible, it is suggested that Older units which have already lived half their life or more may be exempted from retrofits due to various technical constraints Emission control technologies are still in developmental stage, especially for Indian coals, at least 5 7 years should be allowed for compliance NTPC is committed to implement all of the stipulations in the units ordered after issuance of the new norms (07.12.2015).

Thank You Any questions? 31