Transcript Document
1 MUNICIPAL SOLID WASTE (MSW) • MATERIAL RECOVERY FACILITY(MRF) • WASTE TO ENERGY PLANT(WTE) 2 WHAT IS TYPICAL GARBAGE ? 3 AVERAGE WASTE CHARACTERISTIC FOR GARBAGE (% BY WEIGHT) 4 CURRENT LOGISTICS IN MSW HANDLING AND TREATMENT COLLECTION RESIDENTIAL TRANSFER STATION LANDFILL TRANSFER STATION (VOLUME REDUCTION) COMMERCIAL LARGE OBJECTS, CONSTRUCTION MATERIALS, ETC. LANDFILL 5 PROPOSED REPLACEMENT OF TRANSFER STATION WITH MATERIAL RECOVERY FACILITY (MRF) WASTE TO ENERGY PLANT (WTE) 6 THERMAL REDUCTION STATION COLLECTION WASTE TO ENERGY PLANT MRF LANDFILL Main stream Urea injection RESIDENTIAL Material Recovery Facility CONNECT TO TNB GRID Turbine RSF EnvirOcycler Fuel Input COMMERCIAL Heat Recovery Boiler External Dust Control Dioxin Control Unit ID FAN Chimney Steam for ejector ID EVAPORATIVE COOLING TOWER STEAM CONDENSER 0.2 BARs HOT WELL STORAGE Cooling water return Gasification/ Combustion air Water evaporation loss CIRCULATION WATER PUMPS Feed Water Pumps 2 x 100% capacity pumps CONDENSATE EXTRACTION PUMP DEARATOR MAKE UP WATER PUMP -2% of feed water -2 x 100% capacity) Cooling water flow Cooling water Pumps (2 x 100% capacity) DM Water Tank BLOW DOWN -1% of circulation water Cooling water make up pump – 3% of circulation water DM Plant cap=-3% feed water BOTTOM ASH LARGE OBJECTS CONSTRUCTION MATERIALS ETC. LANDFILL 7 100% MSW BIG OBJECTS BAG SPLITTER PLASTICS ( 8-10%) PICKING LINE FERROUS 3% NON-FERROUS 0.9% RECYCLING AND REFUSE SEPARATED FUEL (RSF) PLANT SHREDDER TROMMEL 30% FOOD WASTE/ ORGANICS (TO LANDFILL OR COMPOSTING ) RSF STORAGE OF RSF 2 TO 3 DAYS STORAGE TO HEAT PLANT HOME 8 WHAT IS RSF FUEL IT HAS:- • LESS FUEL PREPARATION • MOISTURE AROUND 60 – 65 % • LOW CALORIFIC VALUE < 1500KCAL/KG • HIGH ASH CONTENT HOME 9 RSF TO BE GASIFIED IN A 2- STAGE GASIFIER WITH CHARACTERISTICS : - HIGH MOISTURE CONTENT - LOW CALORIFIC VALUE HOME 10 EnvirOcycler More photos HOME 11 EnvirOcycler 1st Stage: gentle updraft gasification on very large grate 2nd Stage: vigorous, double vortex, cyclonic combustion Emissions: CO < 1ppm, NOx < 15 ppm, particulate < 100 mg/Nm3 (< 0.125 lb/106 Btu; < 0.04 gr/dscf) Units in continuous operation for 29 years HOME 12 FUEL SOURCE Separated MSW (RSF) Empty Fruit Bunch(EFB) Saw Dust & Timber Waste Partially Dried Municipal Sewage Sludge Rice Husk Cattle Manure Pig Manure Poultry Litter Etc. HOME 13 SIGNIFICANT FEATURES, 1 Four air sources: Underfire air gasifies biomass in the 1st stage Overfire air preheats 1st stage producer gas to ensure ignition in the 2nd stage Primary combustion air ignites the preheated producer gas at the bottom of the 2nd stage Secondary combustion air completes combustion of producer gas in the 2nd stage HOME 14 SIGNIFICANT FEATURES, 2 Very large 1st stage grate area o Resulting in grate temperature < 650 C Essentially zero slag Very low underfire air flow (to gasify RSF/ Biomass) Therefore, very low particulate carry-over from pile HOME 15 SIGNIFICANT FEATURES, 3 Staged combustion permits operating excess air levels to as low as 15% Staged combustion and low temperatures (due to wet fuels) combine to produce virtually zero thermal NOx HOME 16 SIGNIFICANT FEATURES, 4 Dioxins and Furans Destroyed Chlorine can react with cellulose to form dioxins and furans in the 1st stage However, these gases are destroyed in the 2nd stage at 1,100oC No black waterwalls are present to chill – and lock in - dioxins or furans in the 2nd stage HOME 17 SIGNIFICANT FEATURES, 5 The EnvirOcycler can burn RSF and Biomass with moisture contents up to 65% (wet basis) and ash contents up to 35% 5:1 turndown ratio is standard; 9:1 is not uncommon 15 second response time to step change in Btu Demand signal Abort valve permits rapid dumping of products of combustion in an emergency HOME 18 What About Alkali deposits? When agricultural waste was burned in wood residue boilers, boiler tubes became coated with slag-like deposits The deposits were due to condensed salts of Potassium (K) and Sodium (Na) K (vapor temp = 760oC) and Na (vapor temp = o 880 C) vaporized off the potash and soda in the o ash on the 980 C – 1,100oC grate K and Na then formed salts with chlorine and sulphur compounds in the furnace gases HOME 19 Deposit Buildup The K and Na salts condensed and formed sticky, flypaper-like coatings on the boiler tubes Particulate lifted off the grate fuel pile, and up through the furnace by rising products of combustion, adhered to the coated tubes A progressive buildup of alkali deposits ensued, particularly at a change in the flow path of the gases through the boiler Hence the term “alkali deposits” HOME 20 Alkali Deposits – Not in EnvirOcycler Because the EnvirOcycler’s grate temperature o does not exceed 650 C, K and Na do not vaporize Rather, K and Na remain as potash and soda on the EnvirOcycler’s grate and are removed by the built-in ash removal system Similarly, phosphorus in poultry litter, the suspected cause of Pfiesteria outbreaks, also remains on the EnvirOcycler’s grate HOME 21 ELEVATION WASTE HEAT RECOVERY BOILER HOME 22 More photos WASTE HEAT RECOVERY BOILER HOME 23 SELF-REGULATING BRUSHLESS GENERATOR (TYPICAL) TYPICAL STEAM TURBINE More photos - Steam consumption rate - 4.3 kg/hr HOME 24 EMISSIONS CONTROL HOME 25 HOME 26 FABRIC BAG FILTERS Fabric filter with cleaning by back-flushing COLLECTION PRINCIPLE When dust-laden gases flow through a porous fabric, the dust is separated from the carrier gas and deposited on the filter colth. It is removed periodically and falls into the dust hopper. OBJECTIVE To reduce particulate emissions to less than 10mg/Nm3 27 DIOXIN REMOVAL-PRESENT TECHNOLOGY 28 SUMMARY: SHELL DIOXIN DESTRUCTION SYSTEM 29 COMPARISON OF SDS VERSUS HONEYCOMB 30 COMPARISON OF SDS VERSUS HONEYCOMB 31 CRI SCR REACTOR SYSTEM 32 33 TYPICAL DIOXIN DESTRUCTION PERFORMANCE 34 35 36 EMISSIONS Particulate CO NOx Dioxin < < < < 10 mg/Nm3 1 ppm 80 mg/Nm3 0.1 mg/Nm3 VORTEX EFFECT IN EnvirOcycler CLEAN HEAT EMISSION HOME 37 HOME