1 ENGG*4230 Energy Conversion University of Guelph, Fall 2022 • 1 Overview • 2 Review • 3 About the Final Exam Review- 01/12/2022 1.2 Energy Conversion (ENGG* 4230) • The course introduces the technical criteria for the design of efficient energy conversion processes and systems. – Lectures provided theory and examples – Laboratories/Tutorials provided hands-on experience You should now have a better understanding on the following: 1. Introduction to energy conversion and sustainability 2. Fundamentals of Energy Conversion: Energy forms, conversion systems and energy intensity 3. Emission intensity, climate change and energy conversion planning 4. Biomass properties, Various conversion processes 5. Fuel and Combustion Calculations 6. Introduction to Thermal Power Plant 7. Design of Thermal Power Plant: pulverized, fluidized bed, integrated gasifier combined cycle systems, 8. Biochemical biomass conversion 9. Solar energy system design: Thermal and PV 10. Wind Energy system design 11.Geothermal Energy 12.Energy Storage Final Review- 18/10/2022 • 2 1. 3 Energy Production in Canada 2018 3 4 Energy Production in Ontario 2021 4 5 Energy Emissions 5 6 Electricity Emissions 6 7 Coal Plants Wikimedia Commons [Online]. Available: http://upload.wikimedia.org/wikipedia/commons/thumb/4/4a/Coal_fired_power_plant_diagram.svg/1280pxCoal_fired_power_plant_diagram.svg.png 7 8 Coal Plants 1 • Coal plants obviously burn coal • Burning coal produces nitrogen oxide (NOx) and sulfur (SOx) • It will also leave particle pollution – Dust, dirt, smoke, – Sometimes arsenics and other matter • Coal plants can also pollute water – In China, 1/5 of the water is used in “coal washing” – However, “coal washing” reduces the ash content of the coal which means less air pollution 8 9 Coal Plants 2 • The last coal plant in Ontario closed in 2014 • • • • There are 9 coal-fired plants in Canada Most of these plants are phasing out of coal into natural gas Globally there are about 8500 coal plants Quick research – how many coal plants are in your native country? 9 10 Natural Gas Plants • Natural gas is an colourless and odourless gas that burns easily • In Canada, Natural gas is used for heating, hot water heaters, gas burning stoves and BBQs, and even fireplaces 10 11 Natural Gas Plants 1 1. Wikimedia Commons [Online], Available: https://upload.wikimedia.org/wikipedia/commons/4/4c/Jet_engine.svg 11 12 Natural Gas Plants 2 • They operate much like a jet engine • Some plants, called Combined Cycle, will use the heat to produce steam for a steam turbine • Some plants use the excess heat to industrial plants – This is called Co-generation or Co-Gens • Gas is cleaner than coal, however, it does still produce emissions than can be harmful to the environment • According to the US EIA, Gas plants produce 114 pounds of carbon dioxide for every million BTU, while coal will produce 200 pounds and more than 160 pounds of distillate fuel oil 12 13 Hydro Plants Source: https://www.energy.gov/eere/water/types-hydropower-plants 13 14 Hydro Plants 1 • Use the mechanical energy from water and turns it into electrical energy • They can be found at dams, on rivers, and at waterfalls • The water needs to drop from a certain elevation (the head) and drop to spin the turbine • Canada has the second most hydro plants in the world 14 15 Hydro Plants 2 • While hydro plants do not produce any harmful emissions, the dams and reservoirs can cause issues for the aquatic life around them 15 16 Nuclear Plants 16 17 Nuclear Plants 1 • During operation, nuclear plants do not produce any greenhouse gas emissions • The fuel rods are highly radioactive and must be disposed of carefully • In Canada, the used rods are stored in deep pools of water for 7-10 years and then stored in dry storage for …well…a very long time • There are 3 nuclear plants in Ontario – Pickering, Darlington and Bruce – They are all on the great lakes due to their need of immense amounts of water 17 18 Wind Power 18 19 Wind Power 1 • Wind power also does not produce any emissions • Due to the laws of physics (or Betz Law), wind is only capable of 59.3% efficiency • Surprisingly, wind power can only be produced when there is wind! (Usually at a minimum speed of 5 m/s) • While the use blade can be recycled, currently they are just being buried in landfills • The blades can move at speeds of 200 km/h, this has been known to be deadly to birds and bats 19 20 Solar Power 20 21 Solar Power 1 • Does not produce any emissions • Does not produce energy at night?!?!?! • Converts sunlight into electrical energy through photovoltaic (PV) panels • First solar panel was invented in 1883 (but was only 1% efficient) • In 1954 solar panels were used to power satellites and were less than 10% efficient • Today most solar panels are around 20% to 27% efficient • The most efficient solar panel is 47% efficient (just not cost effective yet) 21 1. Overview 22 Energy Conversion • The course introduces the technical criteria for the design of efficient energy conversion processes and systems. It includes the review of boilers and cycles, fuel and combustion calculations, and fundamentals of both traditional and emerging energy conversion processes and systems for production of thermal, mechanical, and electrical energy. Topics include fossil, biomass and nuclear fuels, as well as wind, solar, geothermal energy and fuel cells. Mechanisms for storing energy generated from each of these are also studied. The course also explores conversion of automobile systems, renovation of old fossil fuel fired plant technology, cofiring of opportunity fuels, waste to energy technology, emissions, and economics of energy projects. Review- 18/10/2022 1.1 Course Overview • 2. Review 23 2.1 Introduction to Thermal Power Plant, Design of Thermal Power Plant: pulverized, fluidized bed, integrated gasifier combined cycle systems • Heat Balance and Design of a Boiler • State of Biomass Combustion Technologies: Coal/Waste Combustion Technologies • Torrefaction and Gasification Technologies for Biomass Conversion Introduction to Thermal Power Plant 24 Schematic Diagram of a Power Plant Heat Balance 25 Direct Method This is also known as ‘input-output method’ due to the fact that it needs only the useful output (steam) and the heat input (i.e. fuel) for evaluating the efficiency. This efficiency can be evaluated using the formula Q--Quantity of steam generated per hour in kg/hr. q--Quantity of fuel used per hour in kg/hr. GCV--gross calorific value of the fuel in kCal/kg of fuel Heat Balance 26 Heat given to steam in a boiler • Heat delivered to water Q1 = m (Hsteam –Hfeed) where Hsteam = Enthalpy of superheated steam (kJ/kg) Hfeed = Enthalpy of feed water (kJ/kg) Heat Balance 27 HEAT BALANCE • HEAT INPUT = HEAT UTILIZATION +LOSSES • Q = Q1+ Q2+ Q3+ Q4+ Q5+ Q6+ Q7 + Q8 • Q = Available heat of fuel • Q1= Heat utilized by steam and water • Q2 = heat lost through stack gas • Q3 = Unburned carbon • Q4 = Moisture in fuel • Q5 = Hydrogen in fuel • Q6 = Moisture with air supplied • Q7 = Loss from boiler surfaces • Q8 = sensible heat in ash Heat Balance 28 29 Losses from combustor Dry flue gas loss (Q2) Fuel moisture loss (Q4) Loss due to H2 (Q5) Energy generated from combustion of fuel – Heat delivered to water (Q1) Radiation loss (Q7) Moisture in air loss (Q6) Sensible heat loss due to ash (Q8) Heat Balance Unburned carbon loss (Q3) Equations to Estimate Heat losses • Dry flue gas loss: (Mg*Cpex*tex-Mwa*Cpair*tair)/HHV*100 • Unburned carbon loss: Unburned carbon content*ash*heating value of carbon/HHV*100 • Fuel moisture loss: Mf*(hfg@ex.temp-hwl@in.temp)/HHV*100 • Air moisture loss: Xm*(hfg@ex.temp-hwl@in.temp)/HHV*100 • Moisture from H2 in fuel: 9H*(hfg@ex.temp-hwl@in.temp)/HHV*100 • Sensible heat loss due to ash: Ash*Cpash*tash/HHV*100 • Thermal efficiency of a boiler = 1-sum of all losses Heat Balance 30 Design of a boiler: Steam enthalpy and parameters • Once the pressure schedule of the steam/water circuit is made, the steam/water parameters (Enthalpy) can then be estimated from the available steam table. • The heat duty of each segment (EC, Evaporator, SH, RH etc) can then be calculated once mass flow of steam/water is known. • The total heat duty is the sum of heat duty of all the segments • The fuel consumption can them be calculated by the following equation – Fuel consumption (kg/s) = Total heat duty (kJ/s)/(Thermal efficiency of the boiler*HHV of fuel (kJ/kg)) • The air requirement (kg/s) and flue gas produced (kg/s) can then be calculated afterwards. Heat Balance 31 How to Improve efficiency of boiler • • • • • • • • • • • • Oxygen Trim Systems Flue gas outlet temperature MS temp HRH temp Feed Water Temp Blowdown control Blowdown heat recovery Flash Steam Recovery Steam Trap Leaks Exhaust Draft Control The effect of coal blending on combustion performance Air to fuel ratio control Heat Balance 32 Factors Affecting Boiler Performance The various factors affecting the boiler performance are listed below: • Periodical cleaning of boilers • Periodical soot blowing • Proper water treatment programme and blow down control • Draft control • Excess air control • Percentage loading of boiler • Steam generation pressure and temperature • Boiler insulation • Quality of fuel Heat Balance 33 Design Problem A biomass boiler uses Miscanthus as a fuel with following elemental analysis Element Weight (%) Carbon, C 46.82 Hydrogen, H2 6.14 Nitrogen, N2 0.30 Sulfur, S 0.03 Oxygen, O2 43.40 Ash 3.31 Moisture, Mf 5.78 HHV (kJ/kg Fuel) 19276 34 a. Calculate the boiler efficiency if fuel feed rate is 12.65 kg/s and output of the boiler is 200MWth? b. Find the volumetric capacity (m3/s) of the combustion air fan (forced draft) for the boiler if air is handled at 27 C. Assume excess air (EAC)=20%, moisture in air (Xm) is 1.3%, specific volume at standard temperature and pressure (STP) = 0.7734 m3/kg, Cp air@27C =0.97 kJ/kg.0C and Cp flue gas@150C =1.1 kJ/kg.0C. c. Estimate the flue gas produced in kg/s if the unburn carbon loss is 1.5% Equation: Stoichiometric air required, Mda = [0.1153C+0.3434(H-O/8)+0.043S] kg/kg of dry fuel Here C, H, O, and S to be used in percentage form (For example, C=46.82 and so on) The actual air including excess air (EAC) and moisture (Xm), in air is Mwa = (1+EAC)Mda(1+Xm) kg/kg of dry fuel Here EAC, and Xm to be used in absolute form (For example EAC=0.20 and so on) 35 36 Estimation of higher heating value (HHV) • Channiwala and Parikh (2002) developed the following correlation for HHV based on 15 existing correlations and 50 fuels including biomass, liquid, gas and coal HHV=349.1C + 1178.3H + 100.5S – 103.4O – 15.1N – 21.1ASH Unit: kJ/kg 3 0<C<92%; 0.43<H<25%; 0<O<50%; 0<N<5.6%; 0<ASH<71%; 4745<HHV<55345 kJ/kg Stoichiometric Calculations for Complete Combustion Noting that dry air contains 23.16% O2, 76.8% N2 and 0.04% inert gases by weight, the dry air required for complete combustion of a unit weight of dry hydrocarbon, Mda is given by Mda = [0.1153C+0.3434(H-O/8)+0.043S] kg/kg of dry fuel The actual air including excess air (EAC) and moisture (Xm), in air is Mwa = (1+EAC)Mda(1+Xm) kg/kg of dry fuel 3 37 38 State of Biomass Combustion Technologies Also Coal/Waste Combustion Technologies 39 Why Biomass? ➢ Enormous Resources- Biomass ranks second after large hydro in producing renewable energy in Canada, and creates almost three times as much energy as wind. ➢ Political benefits - e.g. reduced dependency on imported fossil fuels; rural development; energy diversification; ➢ Employment creation- biomass fuels create up to 20 times more employment than fossil fuels. ➢ Stable fuel Price- it has been stable historically and are not directly linked to national or global energy markets. Biomass pricing is not subject to monopolistic control. ➢ Environmental benefits- e.g. mitigation of greenhouse gas emissions, reduction of acid rain, and soil improvement 39 40 Biomass Conversion Technologies Options Combustion Systems are the only commercially available bioenergy technologies with a size ranges from 2 kW to 500 MW 40 41 Basic process flow Biomass/ Coal/ WasteAir Furnac e Boiler Hot Flue Exhaust flue gas gas Ash Thermal energy Furnace type: Mainly Fixed bed types and fluidized bed types Fixed bed systems include manual-fed systems, spreader41 stoker systems, under screw systems, through-screw systems, static grates, and inclined grates Fluidized bed systems include bubbling and circulating varieties. Size Ranges for Combustion Equipment Ref: Preto 2011 42 42 43 Commercialization Status of Biomass Combustion Systems 43 44 Biomass Boilers—Different types Advantages: • Low cost • Small fuel inventory makes for very rapid response to load changes Underbed Stokers Disadvantages: • Moisture content (MC) preferably <30%, not more than 35% • Lack of provision for primary and secondary air supply limits fuel flexibility • Consistent particle size and MC for stable fire 44 45 Wood Combustor Evaluations • Grate Type – Fixed bed • Pin-hole grate • Slopping grate – – – – Travelling grate/chain Reciprocating/stepping grate Vibrating grate Pre-combustor (Two-stage) Grate Evaluation • Better Control • Fuel Flexible • Lower emissions • Higher thermal efficiency • Fluidized bed boilers – Bubbling bed – Circulating bed • Suspension burners 45 46 Fixed Bed Grate • Manual Ash Removal limits size and requires “down time” • Refractory maintenance can be costly • Low air flow rates (overfire air does not penetrate chamber at low flow rates and may cause too much dilution/cooling at low fire leading to increased emissions) 46 Steeping Grates ADVANTAGES: ➢ Some tolerance of fuel type, moisture and particle size ➢ A positive movement of fuel down grate reduces blockages ➢ Better controlled air distribution leads to high efficiency ➢ Modern systems can have a split of 40:60 for undergrate and overfire air distribution DISADVANTAGES: ❖ Large fuel inventory slows response to load changes and increase emissions at low loads ❖ Poor mixing especially when co-firing different fuels ❖ Problems with high moisture fuels (>45% moisture) ❖ Moving elements have problems with 47 rocks and metal 47 Fluidized Bed Technology • “Fluidization is the operation by which solid particles show fluidlike properties through suspension in a gas or liquid” (Kunii and Levenspiel, 1991). • An essential characteristic of a fluidized bed is the liquid-like behavior. With this behavior, a gas-solid mixture bears a linear static pressure distribution, denser objects sink and lighter objects float. • Under the fluidized state, the gravitational force on granular particles is offset by the fluid drag. • The fluidized beds have improved gas-solid mixing and more uniform temperature distribution compared to fixed bed reactors. Fluidization 48 Basics of Fluidization •Static pressure at any height equals weight of bed solids P h = − g p (1 − ) + g − gp •Bed surface is always horizontal •May be drained like a liquid •Particles are well mixed such that a nearly uniform temp is maintained Fluidization 49 Fluidized Bed Principles Features: Ref:Fluidized bed ➢Excellent mixing, ➢High thermal inertia ➢Higher residence time ➢Higher heat transfer ➢Moderate operating temp. ➢Uniform temp. distribution 50 Fluidizations regimes The pressure drop through a fixed bed of loose material, as a function of velocity. It also shows the pressure drop for other fluidization regimes 51 52 BUBBLING REGIME Freeboard: the entire region between the bed surface and the gas outlet. Splash zone: the region just above the bed surface, in which coarse particles fall back down. Disengagement zone: the region above the splash zone, in which both the upward flux and the suspension concentration of fine particles decreases with increasing height. Dilute-phase transport zone: region above the disengagement zone, in which all particles are carried upwards; particle flux and suspension concentration are constant with height. Dilute transport Freeboard H TDH Splash zone Bed (bubbling zone) Fluidization Suspension density What is a CFB Boiler 53 •A type of steam generator where fuels burn in a special hydrodynamic condition called the fluidized state and transfers the heat to the boiler surface via some inert solid particles. It comprises of •CFB loop (combustion chamber, gas-solids separator and standpipe) •Convective loop (back pass heat exchangers) The fluidization is achieved by blowing relatively low-velocity air into a medium such as sand. It exhibits core-annulus structure 53 Circulating Fluidized Bed - Hydrodynamics fast fluidization regime Particle Velocity solids volume fraction wall wall Time-averaged behavior bubbling fluidization regime 54 55 Solids Distribution (CFB) U = 5 m / s , S A / P A = 0 o 6 3 0 2 G ( k g / m s ) s 5 2 5 Average Suspension Density (kg/m3) Bed Height (m) 8 1 5 2 5 4 3 2 2 0 1 5 1 0 5 1 0 0 0 0 1 0 2 0 3 0 4 0 5 0 3 S u s p e n s i o n D e n s i t y ( k g / m ) 6 0 5 1 0 1 5 2 0 2 5 2 S o l i d s C i r c u l a t i o n R a t e ( k g / m s ) 3 0 56 Fluidized bed Systems Courtesy of Metso Power Oy 56 Features (continued) 57 57 58 Benefit of Fluidized bed boiler 58 59 Biomass Boiler Efficiency Comparison 59 Comparison of Stokers with Fluidized Bed 60 60 61 Dust or Suspension Burners To ensure higher combustion efficiency • Moisture content of dust <10% • Particles sizes of dust <1 mm. • The volatile matter content ≥ 80% • Particles should be of flake-like and narrow shape. • Low ash with lower Cl, K, and Na content in ash. 61 62 Pulverised fuel technology 62 Technology comparison of CFB versus pulverized fuel firing for utility power generation 63 63 Why do we select CFB? 64 64 65 65 66 Why should Utility consider Fluidized bed boilers ➢ ➢ ➢ ➢ ➢ ➢ ➢ ➢ Fuel supply is more uncertain and more diverse than ever before Great opportunity for taking advantage of non-traditional fuels Pollution standards are changing. FB boilers are more suited for the change Air pollution norm without combustion penalty makes it ideal for years to come Price of CFB boilers are competitive with bare bone PC boilers Capacity is no longer a barrier. CFB boilers rising to 660 MW CFB can maintain its efficiency and availability with off-design fuels better than PF units More suitable for supercritical operation than PF boilers 66 67 TORREFACTION AND GASIFICATION TECHNOLOGIES FOR BIOMASS CONVERSION 67 68 BACKGROUND Depleting fossil fuel resources and GHG/Global Warming Renewable energy, sustainable fuels Biomass Carbon-neutral, local fuel; energy security Technology barriers to their utilization as energy source 68 69 Promising pre-processing technology 69 Ref: UMEA, 2010 70 Torrefaction ➢ A thermochemical treatment process, similar to roasting or mild pyrolysis ➢ Energy density increases as ~70% biomass remains with 90% of its original energy content Cellulose Cellulose Lignin Lignin Hemicellulose Hemicellulose 1.3 E/M 70 71 Indicative Fuel Properties (Cont.) Parameters Dust Hydroscopic properties Biological degradation Milling requirements Handling properties Product consistency Transport cost Wood Wood pellet Average Limited Hydrophilic Hydrophilic Torrefaction Charcoal Coal Pellets Limited High Limited Hydrophobic Hydrophobic Hydrophobic Yes Yes No No No Special Special Classic Classic Classic Special Easy Easy Easy Easy Limited High High High High High Average Low Average Low 71 72 The added value of torrefaction Higher co-firing Torrefied biomass can directly milled and co-fired with coals. percentages Product is dry (<5%) and has a calorific value of 20-22 MJ/kg. Cost savings in handling and processing The product is brittle and easily breaks down in small particles. Dedicated biomass equipment (hammer mills, silo storage, biomass feeding systems, biomass burners are not needed. Also it is less sensitive to degradation due to hydrophobic nature. Cost savings long in transport The volumetric energy density of torrefied pellets is 16 GJ/m3 compared to 10 G/m3 of wood pellets Torrefaction alone will NOT: Significantly reduce sulfur, chlorine and alkali concentrations of the biomass 72 73 TORREFACTION-PELLETIZATION Moisture: 8% Bulk density: 700 kg/m3 Energy density: 10 GJ/m3 Bulk density: 800 kg/m3 Energy density: 16 GJ/m3 Torrefied Pellets Wood Pellets Biomass collection Moisture: 35% Bulk density: 225 kg/m3 Energy density: 2.5 GJ/m3 Torrefaction Pelletizing Wood Pelletizing Tree logs Chipping Torrefied wood chips Moisture: 4% Bulk density: 300 kg/m3 Energy density: 7.5 GJ/m3 Transportation Torrefaction 73 74 TYPICAL TORREFACTION PROCESS FLOW Raw Material Infeed (chips) Advantage: Two marketable products: Pellets & Torrefied pellets Classifier Rotary Drum Dryer Hammer mill Pelletizer Torrefier Cooler Classifier Rotary Drum Dryer Torrefier Hammer mill Pelletizer Cooler Raw Material Infeed (chips) Advantage: Lower energy cost for hammer mill 74 Torrefaction technologies 75 •Most reactor configuration/technologies applied for torrefaction are proven in other applications (drying, pyrolysis, gasification, combustion). Screw conveyor •All ofdrum them have their own advantages and disadvantages Rotary Belt conveyor reactor reactor reactor •Overall efficiency depends on their design configuration in heat integration in the form of either direct or indirect •Process control (temperature, residence time, particle size, mixing) is the key for better performance of the reactor Moving bed Torbed TurboDryer reactor Microwave 75 reactor Technology status 76 Biomass Conversion Pathways Thermal Excess air Partial air Biological Gasification Physical No Air Pretreatment Combustion A/D Hydrolysis Pyrolysis (Heat & Pressure) Fermentation Heat Fuel Gases (CO + H2) 77 Liquids H2 Ethanol CH4 Liquids 78 Biomass Conversion Pathways Biomass conversion to Biochemicals, Biofuels, and Bioenergy Thermal gasification Chemical looping gasification Dry torrefaction Multi stage gasification Bio-carbon for various application Wet torrefaction /liquefaction Supercritical gasification Anaerobic digestion Dry/steam reforming Syngas fermentation to renewable liquid fuels 78 79 Samples of Torrefaction of agri-residue Tests performed at 2500C temperature and 1 hour residence time Rice husk Sawdust Peanut husks Bagasse A water hyacinth Ref: Dutta, 2010 79 80 Hydrothermal Carbonization 30-80% 15-50% 2-5% 80 81 HTC Inputs and Outputs Biochar Woody Biomass Hog Fuel • Soil amendment Willow Purpose Grown Biomass Miscanthus Hydrochar • Heat and power production Charcoal • Metallurgy applications Wet Biomass Agricultural Biomass Switchgrass Wheat Straw Corn Stover Biocarbon Tomato Vines Corn Husks Activated Carbon • Wastewater treatment 81 82 van Krevelen Diagram 1.8 1.6 H:C (ATOMIC RATIO) 1.4 1.2 1 0.8 Increased Heating Value 0.6 0.4 0.2 0 0 0.2 0.4 O:C (ATOMIC RATIO) 0.6 Feedstock(Treatment)Temp-Time-Pressure CS(raw) CS(HTC)-200-5-Sat. CS(HTC)-200-15-Sat. CS(HTC)-200-30-Sat. CS(HTC)-200-45-Sat. CS(HTC)-230-5-Sat. CS(HTC)-230-15-Sat. CS(HTC)-230-30-Sat. CS(HTC)-230-45-Sat. CS(HTC)-260-5-Sat. CS(HTC)-260-15-Sat. CS(HTC)-260-30-Sat. CS(HTC)-260-45-Sat. CH(raw) CH(HTC)-260-15-Sat. CH(HTC)-260-15-6 CH(HTC)-260-15-7 CH(HTC)-260-15-8 CH(HTC-NW)-260-15-7 0.8 Coal 82 83 83 Biomass gasification process 84 One of the best way to optimize the extraction of energy from biomass and to obtain a standardized gas from very different materials Air, Steam, CO2, and/or O2 CO, H2, CO2, H2O, CH4, C2H4 BIOMASS Low Calorific Value: Medium Calorific Value: + unconverted tars (all organic compound with mass > C6H6) 4 - 6 MJ/Nm3 12 - 18 MJ/Nm3 Using air and steam/air Using oxygen and steam The main challenges of biomass gasification are: • Good control of temperature in the reactor •High heating rate (hundreds of degrees per second) and high temperatures (around 800°C) are necessary to maximize the gas yield •TARS conversion •TARs condense in the cold parts plugging of tubes or agglomeration phenomena •TARS removal by filtration lost of efficiency since they still contain energy 85 Biomass gasification reactors Fixed bed technology Updraft gasifier Downdraft gasifier Fluidized bed technology Bubbling fluidized bed Circulating fluidized bed Cyclone : Bed hot particles : Biomass and char : grid Advantages: simple design, good maturity. Drawbacks: low calorific value gas with a high tar and fines content. Advantages: good gas and solid mixing, uniform temperatures and high heating rates, greater tolerance to particle size range and safer operation due to good temperature control compared to fixed bed gasification Drawbacks: low density biomass fuel (with respect to the bed particles) segregates to the surface of the bed. This segregation phenomenon is increased by the formation of volatiles and gaseous species bubbles around the fuel particle, reducing the conversion rate. Fused ash and tar condensation provokes defluidization. Gasification based process scheme Gasifier Types - III 86 Ref: BTG, 2005 Selected commercial Gasification demonstration Plant ENAMORA, Spain Greve-inChinti, Italy Gussing, Australia Lahti, Finland Tech. BFB CFB Feedstocks Almond shell, industry residue RDF Dual FBCHP CFB, Cofiring Wood chips, wood residues Wood, board, paper, plastics, RDF Rudersdorfe CFB r, Germany SVZ, Fixed, Germany Slagging, Entrained Varnamo, CFB-IGCC Sweden Vermont, Indirect USA CFB DTU, Two stage Denmark fixed bed Biomass Power Fuel: 3500 kW; Electrical: 750 kWe Fuel: 2X15 MW; Electrical: 6.7 MWe Fuel: 8 MW; Heat: 4.5 MWth; Electrical: 2 MWe Fuel: 40-70 MW; Heat: 40-70 MWth; Power: 20 MWe of 176 MWe coal power plant Fuel: 100 MW RDF, oil slurries, mixture of tar and sewage sludge Wood chips, pelletised wood, bark, Wood chips, residue wood, pellets, Wood chips (45% moisture) Fuel: 420 MW; Electrical: 75 Mwe; Chemical: 120 kt/a Methanol Fuel: 18 MW; Heat: 9 MWth; Electrical: 6 MWe Fuel: 44 MW; Heat: n.a; Electrical: 9 MWe Fuel: 70 MW; Heat: 39 MW; Electrical: 17.5 kWe 87 Costs Funding Euro: 1.1 Private million Euro: 20 Own million Euro: 8.7 Public: 60% million Private: 40% Euro: 12 25% by EU million N/A Own Euro: 335 million Euro: 25 million U$: 14 million N/A N/A Public: 23% Private: 77% DOE, FERCO 87 Tar conversion: 88 It can be done thermally or catalytically (a lower process temperature improves control of exhaust species) Cleaned gasification gas contains mostly gas phase (light hydrocarbons + H2, CO2, CO, H2O) 1) 2) Tars and gasification products Biomass feeder system Gasifying gas (air, O2, H2O or CO2) The catalytic tars conversion can both decrease tar production and modify gas composition. There are two ways for catalytic tar rem 1: Primary method: the catalyst is mixed with biomass directly inside the gasifier. Single-stage process 2: Secondary method: the catalyst is placed down stream the gasifier. Dual-stage process Primary methods are more difficult to set up (multiphase catalysis), but reduce the costs of the overall process (reactor set up is simplified). 89 Anaerobic Digestion BOD and COD • Biochemical (or Biological) Oxygen Demand (BOD) and Chemical Oxygen Demand (COD) are both indices of the amount of organic material in a sample of waste liquid. • BOD: is the amount of dissolved oxygen needed (i.e., demanded) by aerobic biological organisms to break down organic material present in a given organic materials sample at certain temperature over a specific time period. It is calculated from the change of dissolved oxygen from the mixtures of waste, aerated water and micro-organisms. BOD depends on the temperature and duration of incubation. It is usually expressed as gm (O2)/m3 of waste water. Accepted standard conditions are 5days at 200C. • COD: Estimates the amount of organic matter by measuring O2 required for complete oxidation of the sample. It gives total organic mater whether it is biodegradable or not. • Therefore, ratio of BOD/COD will give the proportion of biodegradable organic matter in the waste sample. Anaerobic Digestion 90 90 Anaerobic digestion is 91 • a complex biochemical process of biologically mediated reactions (in the absence of air) by a consortia of microorganisms to convert organic compounds (biomass) to methane and carbon dioxide. During the process a part of organic material is removed by the micro-organisms and used to support both life and growth functions • a stabilization process achieving odor, pathogen, and mass reduction. Anaerobic Digestion 91 92 Steps in the Anaerobic Process Biodegradable Particulates 1 1 Proteins and Carbohydrates Lipids 1 1 Volatile Acids (propionic, butyric) 1 Amino acids and simple sugars 2 2 2 Acetic acid 3 H2 and CO2 4 5 Anaerobic Digestion Long chain fatty acids CH 4 and CO2 92 Steps in the Anaerobic Process Biodegradable Particulates Proteins and Carbohydrates Volatile Acids (propionic, butyric) Lipids Amino acids and simple sugars Acetic acid Anaerobic Digestion Long chain fatty acids H2 and CO2 CH 4 and CO2 93 93 Steps in Anaerobic Digestion Hydrolysis Acidogenesis Acetogenesis Methanogenesis Anaerobic Digestion 94 94 Steps in Anaerobic Digestion 95 Particulates solubilized and large polymers Hydrolysis converted to simpler monomers Acidogenesis Simple monomers converted to volatile fatty acids Volatile fatty acids converted to acetic acid, Acetogenesis CO2 and H2 Acetate converted into CH4 and CO2 Methanogenesis while H2 consumed Anaerobic Digestion 95 Steps in Anaerobic Digestion Anaerobic Digestion 96 96 Step 1 - Hydrolysis Anaerobic Digestion 97 97 Hydrolysis • Particulates made soluble and large polymers converted to simpler monomers – Carbohydrates, fats, and proteins • Large molecules (polymers) broken down into smaller molecules (monomers) – Allow passage through bacterial cell wall • Facultative arobes and anaerobes • May be rate limiting step in process if high concentration of particulate organic matter. Anaerobic Digestion 98 98 99 Step 2 – Acidogenesis Anaerobic Digestion 99 Step 2 - Acidogenesis • Sugars, amino acids, and fatty acids converted to C3 and C4 volatile fatty acids (76%), H2 (4%), and acetic acid (20%) • Optimum growth rate occurs near pH 6 • Volatile fatty acids generally not significant consumer of alkalinity • CO2 significant consumer of alkalinity • NH3 produced from amino acids Anaerobic Digestion 100 100 Acetogenesis Anaerobic Digestion 101 101 Step 3 - Acetogenesis • Volatile fatty acids converted to acetic acid (68%) and H2 (32%) • Sensitive to H2 concentration • Syntrophic (mutually beneficial) relationship with the methanogens Anaerobic Digestion 102 102 Step 4 - Methanogenesis Anaerobic Digestion 103 103 Methanogenesis • Obligate anaerobes – methanogens – Tend to have slower growth rates • H2 utilizing methanogens use H2 to produce methane removing H2 from system • Limited pH range 6.7 to 7.4 (sensitive) – importance of alkalinity in system • Sensitive to temperature change Anaerobic Digestion 104 104 Routes to Formation of Methane Hydrogenotrophic methanogens CO2 + 4 H2 → CH4 + 2 H2O Acetotrophic methanogens CH3COOH → CO2 + CH4 Methylotrophic methanogens CH3OH + H2 → Anaerobic Digestion 105 CH4 + H2O 105 Background Concepts • • • • Enzymes Environmental Conditions Alkalinity Toxicity Anaerobic Digestion 106 106 Catalysis & Enzymes • Catalysis - the acceleration of a chemical reaction by some substance which itself undergoes no permanent chemical change. • Catalysts of biochemical reactions are enzymes. – Responsible for bringing about almost all of the chemical reactions in living organisms. Without enzymes, the reactions take place at a rate far too slow for metabolism. – Extracellular and intracellular • Note: Bacteria have specific enzymes for specific tasks and not all bacteria have all enzymes. Anaerobic Digestion 107 107 Bacteria : Environmental Conditions strict tolerant anaerobes anaerobes facultative anaerobes 108 strict aerobes Dissolved Oxygen mesophilic thermophilic Temperature 30 – 35 oC 5.0 acidogens 50 – 60 oC 6.2 pH 6.8 - 7.2 methanogens Toxicity (NH3, H2S, metals) Functional Anaerobic Digestion Inhibitory 108 Fatal 109 Bacteria Hydrolysis Acidogenesis Acetogenesis Methanogenesis Anaerobic Digestion 109 Important Note: • Not all bacteria have same environmental tolerance. • Not all bacteria have same optimum environmental conditions. • Optimum gas production depends on types of substrates. Anaerobic Digestion 110 110 Toxicity 111 • Oxygen: is inhibitory to methanogenic bacteria. Highly reduced atmosphere should be maintained. • Volatile acids: pH should be held constant near neutrality. Neither acetic nor butyric acids have significant effect on hydrogen-utilizing methanogenic bacteria. Propionic acids has a little effect. • Ammonia: Nitrogen from protein released as ammonia [amonium ion, NH4, dissolved free ammonia (more toxic), NH3]. A pH below 7.2 is preferable. • Sulfide: Only soluble sulfide exhibit toxicity. Addition of metal like iron precipitates sulfide and reduces soluble sulfide concentration. Anaerobic Digestion 111 Phased (Staged) Digestion • Digestion process separated into multiple reactors to optimize process • Environmental conditions optimized for specific microorganism population – – – – acid-forming methane-forming thermophilic mesophilic Anaerobic Digestion 112 112 Acid / Gas Phased Digestion • Digester 1 – Low solids retention time to promote growth of acidogens (acid forming bacteria) – pH < 6.0 (optimum growth rate) • Digester 2 – High solids retention time to promote growth of methanogens – pH = 7.0 Anaerobic Digestion 113 113 Temperature Phased Digestion • Thermophilic generally 4 times faster than mesophilic • Mesophilic phase enhances stability Anaerobic Digestion 114 114 Anaerobic digestion 115 Anaerobic digestion is employed to stabilize the sludge produced during wastewater treatment. The sludge may be primary, secondary or mixture of both. Anaerobic digestion is equally applicable to other solids such as animal manure, industrial wasted sludge, etc. During anaerobic digestion the organic matter present in the sludge is biologically converted into CH4, CO2 and NH3. The sludge may be applied continuously or intermittently to the reactor and is allowed to remain in the reactor for a given time. The organic and pathogen content is reduced. Why do we need to stabilize the sludge? 1. 2. 3. 4. Reduce pathogens Eliminate or reduce putrescent matters Eliminate offensive odor Reduce the solid concentration Reduction of organic fraction Anaerobic digester 116 Anaerobic digester is an airtight reactor in which digestion of solid such as sludge and animal manure is carried out. Types of anaerobic digester Standard rate anaerobic digester (Low rate) High rate anaerobic digester Single-stage Two-stage Standard rate anaerobic digester (Low rate) 117 • In standard rate anaerobic digester, the content (sludge) of the digester is usually unheated and unmixed. • The active zone of digestion only occupies 50% of total vol. • Because of no mixing, stratification takes place inside the reactor during digestion. The digested sludge forms a bottom most layer and supernatant above digestion zone Biogas • Operated in batch mode. Gas storage • The sludge detention Scum layer Supernatant layer time is about 30-60 days. • The process is not so popular these days. Sludge inlets Supernatant outlets Actively digesting sludge Digested sludge Sludge outlets Single-stage high rate anaerobic digester 118 • In single-stage high rate anaerobic digester, the contents (sludge) of the digester is heated and mixed completely. • Because of complete mixing and heating , much higher VS loading (kg VS/m3-day) can be applied. • Because of mixing, the supernatant cannot be separated from the digested sludge. About 50% of the applied VS loading transforms to gas. The digested sludge is ½ conc. • Operated in continuous mode or cyclic feeding. • The sludge detention time is about 15-20 days. • The process is operated in mesophilic temperature. Two-stage high rate anaerobic digester 119 • In two-stage high rate anaerobic digester, there are two tanks with the first tank being for actual digestion while the second tank is for separation of digested sludge and supernatant. • The first tank is heated and completely mixed while in the second tank no heating and mixing is done. Both the tanks are usually of same size. • Major gas production takes place in the first tank. However second tank also produces some CH4 • The process is operated in mesophilic temperature. Design of anaerobic digester 120 Anaerobic digesters are simple completely mixed reactors for which SRT and HRT are the same. Hence digester design consists of selecting an appropriate SRT and calculating reactor volume directly from the known sludge flow rate. The selection of appropriate SRT depends on: • Degree of stabilization required • Pathogen inactivation • Digester mixing efficiency Also others factors of importance in selecting minimum SRT are Washout of methanogens, hydrolysis rate of particulate organic matter, etc. . For primary solids, 8-10 days of SRT is reasonably enough for stabilization where as 15-20 days is required to achieve substantial stabilization for waste activated sludge because hydrolysis of waste activated sludge occurs at a slower rate than that of primary solids. Design Factors 121 Anaerobic digester is designed in terms of size by using various approaches. Some approaches are outlined below: 1. 2. 3. 4. Solids retention time (SRT) : denoted by C (days) Volatile solids loading rate : kg VS/m3-day Volume reduction Loading factors based on population Important design parameters for anaerobic digesters Parameters Solid retention time, SRT in days Volatile solids loadings, kg VS/m3-day Digested solids concentrations, % Volatile solids reductions, % Gas production, L/kg VS destroyed Methane content, % Standard rate 30 – 60 0.5- 1.6 4–6 35 – 50 500 - 650 65 High rate 15-30 1.6 – 6.4 4 –6 45 – 55 700-1000 65 Solids retention time (SRT) Anaerobic digester is a completely mixed reactor for which solid retention time (SRT) & hydraulic retention time (HRT) is the same. Influent flow rate (Q), m3/day V, m3 Volume HRT, days = V (m3) = day Flow rate Q (m3/day) For a given SRT (HRT), the size of reactor can be easily determined since flow rate (Q) is known to us. Digester volume, V (m3) = Flow rate (Q) x SRT (C ) 122 Volatile solids loading rate 123 The size of an anaerobic digester can also be estimated based on volatile solids loading rate expressed as kg VS/m3-day. Influent VS kg/day V, m3 Volatile solids loading rate, = (kg VS/m3- day) Influent VS (kg/day) Reactor volume (m3) For a given volatile solids loading rate, the size of reactor can be easily determined since influent VS (kg/day) is known to us. Digester volume, V (m3) = Influent VS (kg/day) Volatile solids loading rate,(kg VS/m3- day) Example: 124 A high rate anaerobic reactor is employed to stabilized primary and secondary sludge at mesophilic temperature. The primary sludge flow rate is 500 m3/day with total solids content of 5% of which 68% is volatile. The secondary sludge flow rate is 1250 m3/day at a total solids content of 1% of which 75% is volatile fraction. Assume the specific gravities of primary and secondary sludge are 1.02 and 1.01 respectively. The minimum SRT of the digester should be 12 days and allowable VS loading rate is 2.5 kg VS/m3-day. What is the total VS in kg/day? Determine the volume of digester in m3. Solution: (a) Find mass of sludge produced: Wt. of dry solids (kg/d), W = V x x S x P (m3/d) V = Volume of sludge produced = Density of water (kg/m3) S = specific gravity of sludge P = % of solids expressed in decimal 125 Primary sludge dry solid mass, kg/day = 500 x 1000 x.05 x 1.02 = 25500 kg/day Volatile solids in primary sludge , kg VS/day = 25500 x 0.68 = 17340 kg VS/day Secondary sludge dry solid mass, kg/day = 1250 x 1000 x.01 x 1.01 = 12625 kg/day Volatile solids in secondary sludge , kg VS/day = 12635 x 0.75 = 9468.75 kg VS/day Total Volatile solids = 17340 + 9468.75 = 26808.75 kg VS/day 126 . (b) Size of digester Based on SRT: Total volume of sludge = 500 + 1250 = 1750 m3/day Given SRT = 12 days Digester volume = 1750 x 12 = 21000 m3 Based on volatile solids loading: Total Volatile solids = 26808.75 kg VS/day Given VS loading = 2.5 kg VS/m3-day Digester volume = 26808.75/2.5 = 10723.5 m3 Since the volume based on SRT is much higher than that based on VS loading rate. SRT governs the design of digester. Thus By choosing higher volume, the possibility of biomass washed could . Digester Shape • Rectangular • Cylindrical 127 • Egg-shaped Sludge outlet Sludge inlet Biogas recirculation Rectangular digesters are not so common because of difficulty of mixing the content uniformly. This type of shape is suitable for low rate digesters in remote areas where resources are scare (energy) and land is available at cheaper price. Cylindrical shape anaerobic digester Cylindrical shape digesters are quite common. The mixing is much better than rectangular shape digester. The digesters diameter could be more than 6 m but less than 38 m and depth as high as 14 m. The bottom is conical in shape to (slope 1:4) facilitate sludge draw off. 128 Egg-shaped digester Egg-shaped digesters have many advantages: • Better mixing • No cleaning required as there is no accumulation of grit • Better control of scum layer • Smaller land area requirement 129 Gas production 130 The anaerobic digestion of organic waste produces biogas which contains 65-70% CH4, 25-30% CO2 (by volume) and small amount of N2, H2, H2S etc. Gas production can be estimated from the percentage of volatile solids reduction. 0.75- 1.12 m3 of gas is produced for every one kg of VS destroyed. Gas production depends on types of sludge as primary sludge usually have higher gas production rate than secondary sludge, also on the biological activity in the digester. Gas production rate indicates whether the digester is well operated. Optimum C/N=20-30 Gas production 131 a b 3c n a b 3c n a b 3c Cn H aOb Nc + n − − + H 2O → + − − CH 4 + − + + CO2 + cNH 3 4 2 4 2 8 4 8 2 8 4 8 Primary solids: C10H19O3N + 4.5 H2O → 6.25 CH4 + 3.75 CO2 + NH3 Secondary sludge: C5H7O2N + 2 H2O → 2.5 CH4 + 2.5 CO2 + NH3 Digester Mixing Smooth functioning of digester depends of proper mixing of its contents. Mixing is important for the following reasons: • Mixing helps to maintain the better contact between substrate and microorganisms • Maintains uniform temperature within the digester • Prevents settling of grit matters • Avoids excessive built-up off scum layer Digester mixing can be achieved by: 1. Bio-gas recirculation 2. Mechanical stirring 3. Mechanical pumping 132 Digester heating 133 High rate anaerobic digesters are operated at mesophilic temperature range which therefore requires heating the digester. The heat requirements for digesters consist of: 1. To raise the temperature of incoming sludge to digestion tank temperature. 2. To compensate the heat losses through walls, floors, and roof of the digester 3. To make up losses that might occur in the piping between the source of heat and tank. Solar Thermal Energy 135 Energy balance on a solar collector absorber / receiver 136 Performance of a typical flat-plate thermal collector (ambient temperature 25°C) The resulting plot will be a straight line only if conditions are such that FR, UL and (τ α) are constants. ) 137 Example ⚫ A flat place collector measuring 2m X 0.8m has a loss resistance rL (1/UL) = 0.13 m2kW-1 and a plate transfer efficiency of 0.85. The glass cover has transmittance of 0.9 and the absorptance of plate is 0.9. Water enters at a temperature of 40C. The ambient temperature is 20C and the irradiance in the plane of the collector is 750 Wm-2. Calculate the flow rate needed to produce a temperature rise of 40C. 138 139 Example: The figure below provided the results of a performance test for a single-glazed flat-plate collector. The transmissivity of the glass is 0.90, and the absorptivity, α, of the surface is 0.92. For the collector, find: (a)The collector heat removal factor, FR (b) The overall conductance, UL in Btu/ft2°F. (c)The rate at which the collector can deliver useful energy when the irradiation incident on the collector per unit area is 200 Btu/ft2h, the ambient temperature is 30°F, and the inlet water temperature is 60°F (d) The collector temperature when the flow rate is zero. Fig.: Flat-plate solar collector performance data 140 SOLAR PHOTOVOLTAICS AND SYSTEM DESIGN PV CELLS Single crystal Si Amorphous Si Polycrystalline Si Polymer 141 Dye-sensitized cell Cd Te CuInSe2 HOW A PHOTOVOLTAIC CELL WORK How a photovoltaic cell work in 3 stages is shown in this figure numbered 1, 2 and 3 142 PHOTOVOLTAIC EFFECT 143 The photovoltaic effect produces free electrons that must travel through conductors in order to recombine with electron voids, or “holes.” 144 SOLAR PHOTOVOLTAIC ❖ Direct conversion of radiation to electricity – Not all are designed for it………………… ❖ Semiconductor technology – Similar to diode or transistor – Combination of positively and negatively doped silicon – Radiation provides energy to allow electrons to move – Generates an electric potential ❖ Each solar cell generates ~0.5 V • Put many in series to get 12 or 24 V panels • If shade one cell, acts as diode, entire series stops generating 144 145 SOLAR PHOTOVOLTAIC 145 146 SOLAR ELECTRICITY GENERATION ❖ Standard test conditions – 1000 W/m2 – Defined spectrum – 25°C Solar Photovoltaic ❖ Power output depends on load – Many combinations of voltage and current possible – Good charge controllers optimize load 146 SILICA SAND TO SOLAR PV SYSTEM + = Solar module PV inverter 147 FUNDAMENTAL SOLAR CELL PARAMETERS 148 (a) Short circuit state p dark current J photocurrent electron light Vmax Maximum-power rectangle photo current n V Open circuit voltage Voc hole (b)Openpcircuit state Jmax Short circuit current Jsc light n Voc Typical quantum efficiency patterns for a-Si and μc-Si 1 Q.E. Jsc Voc FF η QE(λ) μc-Si 0.8 Jsc: short circuit current Voc: open circuit voltage 0.6 Fill factor FF Conversion efficiency η 0.4 a-Si 0.2 0 400 600 800 Wavelength (nm) 1000 1200 FF = = Quantum efficiency QE(λ) Vmax J max Voc J sc Voc J sc FF 100 (%) Pin QE ( ) = 1 hc I sc ( ) q P ( ) Pin, P(λ): incident irradiation 149 SOLAR CELL CHARACTERISTICS Maximum power point (MPP) depends on: • Temperature • Irradiance • Solar cell characteristics Fill factor → Performance of solar cell Wilson s. 209 Efficency coefficent PV PERFORMANCE CURVE (I-V) 150 An I-V curve illustrates the electrical output profile of a PV cell, module, or array at a specific operating condition. PV PERFORMANCE CURVE (P-V) A power versus voltage curve clearly shows the maximum power point. 151 PV PERFORMANCE 152 (I -V RESPONSE TO SOLAR RADIATION) Voltage increases rapidly up to about 200 W/m2, and then is almost constant. Current and maximum power increase proportionally with irradiance. PV PERFORMANCE TEMPERATURE RESPONSE OF SOLAR CELL Increasing cell temperature decreases voltage, slightly increases current, and results in a net decrease in power. 153 PV PERFORMANCE I-V RESPONSE TO NUMBER OF CELLS 154 155 TECHNIQUES TO IMPROVE CELL EFFICIENCY • • • • • Stacking (Multi-junction) Concentrating PV (Mirrors or lenses) Reflectors Si spheres Cylindrical modules Source: www.waoline.com Source: Sharp Solar Source: Solyndra 155 156 Example: The specification of a SILFAB SLA-P polycrystalline PV module (SLA 245 P) is given below: Electrical Specifications-Standard Test Units Values Module Power (Pmax) Wp 245 Maximum power voltage (Vpmax) V 30.2 Maximum power current (Ipmax) A 8.11 Open circuit voltage (Voc) V 37.3 Short circuit current (Isc) A 8.65 Module efficiency % 15.0 Maximum system voltage (UL) VDC 1000 Series fuse rating A 15 Power tolerance Wp -0/+5 Temperature Coefficient Isc %/K 0.06 Temperature Coefficient Voc %/K -0.34 Temperature Coefficient Pmax %/K -0.40 NOCT (+/- 2 °C) °C 41 Operating temperature °C -40/+85 Conditions, STC (Solar Irradiance: 1000 W/m2, Air Mass, AM 1.5, Temperature 25°C) Temperature Ratings Find the temperature dependence of solar cell efficiencies at maximum power point (mpp) for the temperatures of 45°C and 65°C. 157 WIND ENERGY SYSTEM DESIGN 157 CLASSIFICATIONS OF WIND ENERGY CONVERSION SYSTEMS Wind Mills If the mechanical energy is used directly by machinery, such as a pump or grinding stones, the machine is usually called a windmill. 158 Wind Turbine If the mechanical energy is then converted to electricity, the machine is called a wind generator 158 TYPES OF WIND TURBINES Vertical Axis Wind Turbine (VAWT) Compared with the horizontal are available commercially. 159 Horizontal Axis Wind Turbine (HAWT) axis type, very few vertical axis 159 160 SIZES AND APPLICATIONS Small (10 kW) • Homes • Farms • Remote Application Intermediate (10-250 kW) • Village Power • Hybrid Systems • Distributed Power Large (660 kW - 2+MW) • Central Station Wind Farms • Distributed Power • Community Wind 160 L05.2 Wind Resources 161 Where, U*: Friction Velocity • K: Von Karman’s Constant (e.g. 0.4~0.41) Z, Z0: Height U: Wind speed 161 • L05.2 Wind Resources 162 162 • L05.2 Wind Resources 163 163 164 Example 1: L05.2 Wind Resources The anemometer at the Elora weather station is at a height of 10 m above ground, surrounded by a large flat expanse of open grass-filled hay field. It is reading a steady wind speed of 5 m/s. The time is 12 noon solar time, and the sun is shinning brightly. • Calculate the maximum possible power per swept area (e.g. P/A) that a wind turbine could produce in these conditions if the turbine had a hub height of 50 m. Clearly state and explain any assumptions you use to make your estimate. 164 • L06.1 Wind Turbines 1 165 165 TURBINE MECHANICAL POWER VERSUS WIND SPEED CURVE 166 166 EFFICIENCY IN EXTRACTING WIND POWER 167 Betz Limit & Power Coefficient: Power Coefficient, Cp, is the ratio of power extracted by the turbine (PT)to the total contained in the wind resource(PW), Cp= PT/PW. Turbine power output PT = ½ * ρ * A * v3 * Cp For utilization of wind power, wind turbine should take as much power from the wind as possible. The turbine slows the speed from v1 to v2 and uses the corresponding power differences. PT = ( 1 m v12 − v 22 2 ) Power utilization efficiency is defined as PTactual/PTideal = Cp/Cpmax The Betz Limit is the maximal possible Cp = 16/27 59% efficiency is the BEST a conventional wind turbine can do in extracting power from the wind. 167 • L06.1 Wind Turbines 1 168 168 Example 2: 169 Assume • Turbine: 2 blades, 10 m rotor diameter • Wind: T= 293 K, Pressure=101.3 kPa, U=12 m/s Find a) Power of incoming wind b) Maximum power theoretically available in wind c) Reasonable value for attainable power d) Rotor speed required e) Torque produced by rotor 169 170 Geothermal Overview 171 What is geothermal energy ❖ The term geothermal comes from the Greek geo meaning earth and therine meaning heat thus geothermal energy is energy derived from the natural heat of the earth ❖ High-temperature underground reservoirs of water or steam, heated by an upwelling of magma ❖ We tap these reservoirs which heats the water, which turns the turbines and creates electricity 171 Heat from the Earth’s Center • Earth's core maintains temperatures in excess of 5000°C – Heat from gradual radioactive decay of elements • Heat energy continuously flows from hot core – Conductive heat flow – Convective flows of molten mantle beneath the crust. • Mean heat flux at earth's surface – 16 kilowatts of heat energy per square kilometer – Dissipates to the atmosphere and space. – Tends to be strongest along tectonic plate boundaries • Volcanic activity transports hot material to near the surface – Only a small fraction of molten rock actually reaches surface. – Most is left at depths of 5-20 km beneath the surface, • Hydrological convection forms high temperature geothermal systems at shallow depths of 500-3000m. http://www.worldbank.org/html/fpd/energy/geothermal/technology.htm 172 GEOTHERMAL RESOURCE TYPES 173 Different Geothermal Energy Sources ❖ As the name implies these are reservoirs of hot underground water. There is a large amount of them in the NA, but they are more suited for space heating than for electricity production. ❖ In this case a hole dug into the ground can cause steam to come to the surface. This type of resource is rare in the NA. ❖ In this type of reserve, brine completely saturated with natural gas in stored under pressure from the weight of overlying rock. This type of resource can be used for both heat and for natural gas. 173 GEOTHERMAL RESOURCE TYPES 174 Different Geothermal Energy Sources ❖ At any place on the planet, there is a normal temperature gradient of +300C per km dug into the earth. Therefore, if one digs 20,000 feet the temperature will be about 1900C above the surface temperature. This difference will be enough to produce electricity. ❖ This type of condition exists in 5% of the NA. It is similar to Normal Geothermal Gradient, but the gradient is 400C/km dug underground. ❖ No technology exists to tap into the heat reserves stored in magma. The best sources for this in the NA are in Alaska and Hawaii. 174 Methods of Heat Extraction http://www.geothermal.ch/eng/vision.html 175 176 Types of Geothermal Direct use Indirect use • Residential Heating • Dry Steam • Industrial and commercial • Flash Steam building heating • Binary System • HDR • Combined Power Plant – Binary and Flash Alternate •Combined System: Uses Power Plant with Direct Use •Coproduced System Geothermal Heat Pump http://www.worldenergy.org/wec-geis/publications/reports/ser/geo/geo.asp 177 Heat Pumps • Residential and commercial/industrial heating or cooling • 3 separate closed loop systems http://www.nextenergy.ca/how-it-works-flash.htm • 30 000 homes with geothermal heat pumps • Over 3000 commercial and industrial buildings http://www.nextenergy.ca/how-it-works-flash.htm 178 Residential Economic Factors • Reduce the heating costs of a home by 60 to 70% • Dependent upon vertical or horizontal system • Dependent upon size of house and where it is located geographically http://www.newenergynexus.com/473/geothermal-pump-cost 179 Geothermal District Heating Southhampton geothermal district heating system technology schematic Boyle, Renewable Energy, 2nd edition, 2004 180 Direct Heating Example Boyle, Renewable Energy, 2nd edition, 2004 181 In-direct Use http://www.bbc.co.uk/scotland/learning/bitesize/standard/physics/energy_matters/supply_and_demand_r ev4.shtml 182 Reservoirs • Hot water reservoir – Direct heat • Natural steam reservoir – Electricity and direct heat • Geo-pressure reservoir – Brine solution of water and steam or http://www.springerlink.com/content/u633m624r2j3p452/fulltext.html CH4 • Created from rain water – Energy and CH4 reserve – Penetrates earths crust and stored between two impermeable rock layers 183 184 Dry Steam http://www.infinityturbine.com/ORC/Geothermal.html • Steam travels directly from production well to injection well at roughly 56 m/s with a temperature of 180-225⁰C at 4 to 8 MPa • To produce 1 KWhe need about 6.5 kg of steam, 55MW plant uses 100 kg of steam per second • Reservoirs maintained naturally and with controlled flow rate 185 Flash Steam Single Flash • Brine mixture containing mainly water above 182⁰C • Most common • Can use 6 to 9 tonnes of steam per hour • Output range 5 to 100 MW http://mitraco-surya.com/contents/geothermal/techniques/ http://www.infinityturbine.com/ORC/Geothermal.html 186 Double Flash • Same procedure as single flash with additional turbine and flash tank • Brine remaining flows into injection well • Second pressure drop produces lower pressure steam • Increases efficiency by 20 to 25% • Costs only increase by 5% Double Flash Schematic Boyle, Renewable Energy, 2nd edition, 2004 187 188 APPLICATIONS OF GEOTHERMAL Binary Cycle Electric Power Generation ❖ Used in geothermal areas where geothermal fluid is at moderate temperatures ❖ Hot geothermal fluid and a binary fluid pass through heat exchanger ❖ Binary fluid has much lower boiling point than water, thus heat from the geothermal fluid causes binary fluid to flash ❖ Flash steam drives turbine/generator 188 Binary Cycle Power Plants • Low temps – 100o and 150oC • Use heat to vaporize organic liquid – E.g., iso-butane, iso-pentane • Use vapor to drive turbine – Causes vapor to condense – Recycle continuously • Typically 7 to 12 % efficient • 0.1 – 40 MW units common http://www.worldenergy.org/wec-geis/publications/reports/ser/geo/geo.asp 189 Binary Cycle Schematic Boyle, Renewable Energy, 2nd edition, 2004 190 Binary Plant Power Output http://www.worldbank.org/html/fpd/energy/geothermal/technology.htm 191 Combined Power Plant • Uses combination of binary with additional system • Can produce 10 to 100 MWe • Increases efficiency of binary • 2 configurations http://mitraco-surya.com/contents/geothermal/techniques/ 192 Direct and Indirect (cogeneration) http://mitraco-surya.com/contents/geothermal/techniques/ 193 Single Flash Plant Schematic http://www.worldbank.org/html/fpd/energy/geothermal/technology.htm 194 195 http://www.worldbank.org/html/fpd/energy/geothermal/technology.htm Binary Cycle Power Plant http://www.worldenergy.org/wec-geis/publications/reports/ser/geo/geo.asp 196 Flash Steam Power Plant http://www.worldenergy.org/wec-geis/publications/reports/ser/geo/geo.asp 197 Efficiency of Heat Pumps Boyle, Renewable Energy, 2nd edition, 2004 198 199 ENERGY STORAGE Energy Storage ⚫ Energy is stored to use it at a different time than when it was generated ⚫ The process of converting the energy to storable form means that some energy is lost due to inefficiency and heat ⚫ Additional energy is lost when the energy is released or recovered due to a second inefficiency ⚫ Ideally, storage is avoided to have a more efficient process ⚫ Time-of-day metering is likely in the future as metering becomes electronic and inexpensive (like a thermostat) ⚫ Shifting the energy from usage peaks to low-use times helps the utility, and customers would be rewarded by lower charges 200 Energy Storage 201 ⚫ Renewable energy is often intermittent (like wind and sun), and storage allows use at a convenient time ⚫ Compressed air, flywheels, weight-shifting (pumped water storage) are developing technologies ⚫ Batteries are traditional for small systems and electric vehicles; grid storage is a financial alternative ⚫ Energy may be stored financially as credits in the electrical “grid” Electrochemical Batteries ⚫ Batteries (groups; from artillery guns) of cells are used separately or in a case containing several cells; a 12V car battery has six 2V cells inside the case ⚫ Large batteries are often use separate 2V cells placed next to each other in a rectangle ⚫ Various cell chemistries are used ◆ Lead-acid; Nickel-cadmium; Lithium ◆ Nickel-metal hydride ◆ Zinc-air ⚫ Best suited to storage periods of 1 second to 60 days ⚫ Self-discharge and sulphation occur with time ⚫ Desulphator circuits can reduce sulfates for longer life 070403 202 Mechanical Energy Storage Three Types of Storage ⚫ Pumped hydroelectric storage (PHS) ⚫ Compressed air energy storage (CAES) ⚫ Flywheels 203 Ultracapacitors 204 ⚫ Ultracapacitors are very high capacitance units ⚫ Best suited to storage periods of 0.1 second to 10 seconds ⚫ Stored energy is 0.5 C V2 ⚫ Capacitances now reach 2.7 kF (kilofarad) ⚫ Carbon electrode surface areas 1000m2 to 2000m2 per gram provide high capacitance ⚫ Electrolytes are sulfuric acid or potassium hydroxide 030331 http://aries.www.media.mit.edu/people/aries/portable-power/ 205 Supercapacitors • Ultracapacitors = Supercapacitors • Two metal plates that are coated with a sponge-like, porous materi called activated carbon • Immersed in an electrolyte made of positive and negative ions dissolved in a solvent • One electrode is positive, and the other is negative • During charging, ions from the electrolyte accumulate on the surface of each carbon-coated plate 205 Image from e-motec.net 206 Supercapacitors - Pros • Fast energy storage • Very long lifespan (upwards of 1 million life cycles) • Charge and discharge very quickly • Lighter than a battery • Can work in extreme temperatures (-40°to 65 ° ) • Does not contain harm acids or metals • Won’t explode 206 207 Supercapacitors - Cons • Low energy density (it doesn’t run for very long) • High self-discharge rate • Can only store about 5% of the energy of a Li-Ion battery • If an ultracapacitor was used for your cell-phone, your battery would basically last forever, however, it would need to recharged every 90 minutes 207 208 Supercapacitors - Future • Currently, ultracapacitors are great for short bursts of energy • Great for the acceleration of an electric vehicle • Peugeot, Lamborghini and Mazda are currently using them for start/stop systems • Ultracapacitors may be used in conjunction with batteries – used for regenerative braking and periods of acceleration • Video: • https://youtu.be/-7T-6XdiRTw Lamborghini Sian – image from Forbes 208 Superconductors ⚫ New technology uses high temperature superconductors (HTSC) ⚫ HTSC operate at -1960C or -3210F ⚫ Diamagnetism- creates a field of opposition to a magnetic field ⚫ Hybrid systems use conventional magnets to levitate and superconductors to stabilize 209 Superconductors ⚫ Since a superconductor has essentially zero resistance, a current once started will flow “forever” ⚫ At a later time, energy could be extracted from the superconductor ⚫ Since the superconductors must be kept far below usual air temperature (~20K to 80K), energy must be used to compress the gas and make it liquefy ⚫ Newer superconductors are being investigated to find ones with a higher critical temperature near room temperature 080331 http://www.accel.de/pages/2_mj_superconducting_magnetic_energy_storage_smes.html 210 Superconductor Example 211 ⚫ A current is induced in the superconductor toroid by inserting a magnet briefly ⚫ Once replaced in the liquid nitrogen, the current circulation can be detected by a compass ⚫ Current decay is on the order of 50% in 1020 years 030331 http://www.imagesco.com/articles/supercond/08.html Ice Thermal Energy Storage 212 ⚫ Air conditioning systems have a high afternoon load to offset the sun heating of the building and the higher outside temperature ⚫ Freezing ice during the night provides a latent heat absorber at lower energy prices, assuming demand charges or time-of-use rates are imposed ⚫ During the day, the ice is melted as the refrigerant is condensed as it passes through pipes in the ice ⚫ The overall process thus provides air conditioning at a lower cost ⚫ Bayside High School in Palm Bay FL uses this method 080331 Issues and Trends 213 ⚫ Energy storage provides energy at a different time than when it was generated (time-shifting) ⚫ Conventional storage systems such as batteries and pumped hydro continue to dominate due to cost ⚫ Short-term storage or energy-smoothing devices like flywheels and ultracapacitors work well in the 10-second time range ⚫ Unneeded generators are often kept in “spinning reserve”, motoring without load to act as generators if additional power is required (air and bearing losses) ◆ This also stores reactive power (v.a.r.s or vars) ⚫ Energy storage will smooth peaks and valleys of availability, but load shifting by the users is more useful 070403 Energy Storage ⚫ Energy storage is to be avoided due to the losses, but may be economic when load time-shifting is possible ⚫ Energy must be stored in vehicles since they cannot obtain sufficient power from wind or sun on the vehicle ◆Special student SunRayce PV cars are fragile and light, and cannot be used in normal highway traffic without a significant death rate ◆ Protected by team cars travelling with them ⚫ Newer technologies may increase energy storage density at a lower cost; both are needed for a viable product 080331 214 215 ❖ Fuel and Combustion Calculations ❖ Introduction to Thermal Power Plant ❖ Design of Thermal Power Plant: pulverized, fluidized bed, integrated gasifier combined cycle systems ❖ Biochemical biomass conversion ❖ Solar energy system design: Thermal and PV ❖ Wind Energy system design ❖ Geothermal Energy ❖ Energy Storage 1. Review- 18/10/2022 Final Exam ( Topics) 216 • Good Luck with your Final Exam