Program for North American Mobility In Higher Education PIECE MODULE 14. “Life Cycle Assessment (LCA)” 4 steps of LCA, approaches, software, databases, subjectivity, sensitivity analysis, application to a classic example. NAMP PIECE Tier III Open-ended problem Module 14 – Life Cycle Assessment 2 NAMP PIECE Prerequisites for tier What are the prerequisites for this tier? It is further assumed that students already have an introductory- level background in Life Cycle Assessment (LCA) (from Tier I and Tier II) and the basic knowledge in petrochemical processes, such as would normally be part of any undergraduate engineering curriculum. Module 14 – Life Cycle Assessment 3 NAMP PIECE Statement of intent What is the purpose of this module? Open-Ended Design Problem. Is comprised of an openended problem to solve real-life application of LCA to the oil and gas sector. The global aim of that problem is to quantify the total environmental benefits and drawback of a process. Module 14 – Life Cycle Assessment 4 NAMP PIECE References Spath and Mann. (2001) ”Life Cycle Assessment of Hydrogen Production via Natural Gas Steam Reforming“. National Renewable Energy Laboratory. Spath and Mann. (1999) “Life Cycle Assessment of Coal-fired Power Production”. National Renewable Energy Laboratory. Mann and Spath. (1997) “Life Cycle Assessment of Biomass Gasification Combined-Cycle System”. National Renewable Energy Laboratory. Rojey A., Minkkinen A., Arlie J.P. and Lebas E. “Combined Production of Hydrogen, Clean Power and Quality Fuels”. Institut Français du Pétrole (IFP). Module 14 – Life Cycle Assessment 5 NAMP PIECE References D. Gray, G. Tomlinson, “Opportunities For Petroleum Coke Gasification Under Tighter Sulfur Limits For Transportation Fuels,” Presented at the Gasification Technologies Conference, San Francisco, California, October 8–11, 2000 H. Baumann, A.M. Tillman(2004). ‘’The hitch Hicker’s Guide to LCA. An orientation in life cycle assessment methodology and application’’. Studentlitteratur AB. Lund, Sweden The Environmental Foundation Bellona : http://www.bellona.no/en/energy University of Newbrunswick (Canada) (Petroleum and Natural Gas Processing): http://www.unb.ca/che/che5134/smr.htm Module 14 – Life Cycle Assessment 6 NAMP PIECE Tier III: Content Tier III is broken in six parts: • • • • • • Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent Report Structure Recommendations Index Unlike the previous two sections, this section does not have a quiz. The student must interpret the results of the above work and elaborate a succinct project report (15 - 20 pages). Module 14 – Life Cycle Assessment 7 NAMP PIECE Tier III: Units of measur Metric units of measure are used. Therefore, material consumption is reported in units based on the gram (e.g., kilogram or metric tonne), energy consumption based on the joule (e.g., kilojoule or megajoule), and distance based on the meter (e.g., meter). When it can contribute to the understanding of the analysis, the English system equivalent is stated in parenthesis. The metric units used for each parameter are given below, with the corresponding conversion to English units. Mass: kilogram (kg) = 2.205 pounds Metric tonne (T) = 1.102 ton (t) Distance: Meter (m) = 6200 mile = 3281 feet Area: hectare (ha) = 10,000 m2 = 2.47 acres Volume: cubic meter (m3) = 264.17 gallons normal cubic meters (Nm3) = 0.02628 standard cubic feet (scf) at a standard temperature & pressure of 15.6°C (60°F) and 101.4 kPa (14.7 psi), respectively Module 14 – Life Cycle Assessment 8 NAMP PIECE Tier III: Units of measur Pressure: kilopascals (kPa) = 0.145 pounds per square inch Energy: kilojoule (kJ) = 1,000 Joules (J) = 0.9488 Btu Gigajoule (GJ) = 0.9488 MMBtu (million Btu) Terajoule (Tj) = 1.0 x 109 Joules (J) kilowatt-hour (kWh) = 3,414.7 Btu Gigawatt-hour (GWh) = 3.4 x 109 Btu Power: megawatt (MW) = 1 x 106 J/s Temperature: °C = (°F - 32)/1.8 Hydrogen Equivalents: 1 kg H2 = 423.3 scf gas = 11.126 Nm3 gas Module 14 – Life Cycle Assessment 9 NAMP PIECE Tier III: Abbreviations and Te Btu CO2-equivalenceEIA GWP HHV HTS IPCCkWh LCA LHV LTS MMSFCD MW N2O Nm3 NMHCs NOx NREL PSA SMR SOx Stressor Stressor category wt% - British thermal units Expression of the GWP in terms of CO2 for the following three components CO2, CH4, N2O, based on IPCC weighting factors Energy Information Administration global warming potential higher heating value high temperature shift Intergovernmental Panel on Climate Change kilowatt-hour (denotes energy) life cycle assessment lower heating value low temperature shift million standard cubic feet per day megawatt (denotes power) nitrous oxide normal cubic meters non-methane hydrocarbons nitrogen oxides, excluding nitrous oxide (N2O) National Renewable Energy Laboratory pressure swing adsorption steam methane reforming sulfur oxides, including the most common form of airborne sulfur, SO2 A term that collectively defines emissions, resource consumption, and energy use; a substance or activity that results in a change to the natural environment A group of stressors that defines possible impacts percentage by weight Module 14 – Life Cycle Assessment 10 NAMP PIECE Tier III: Outline 1. Description of the context: Hydrogen production via natural gas steam reforming 2. Problem statement 3. Statement of the intent a. System boundaries b. Major assumptions c. Data 4. Report Structure 5. Recommandations 6. Index Module 14 – Life Cycle Assessment 11 NAMP PIECE Tier III: Outline 1. Description of the context: Hydrogen production via natural gas steam reforming Module 14 – Life Cycle Assessment 12 NAMP PIECE 1. Description of the context: Hydrogen production via natural gas steam reforming 1.1. Hydrogen (H2) Hydrogen is used in a number of industrial applications, with today’s largest consumers being ammonia production facilities (40.3 %), oil refineries (37.3%), and methanol production plants (10.0%). Because such large quantities of hydrogen are required in these instances, the hydrogen is generally produced by the consumer, and the most common method is steam reforming of natural gas. The figure below shows a simplified flowsheet of the process utilised in this context for hydrogen production. Module 14 – Life Cycle Assessment 13 NAMP PIECE 1. Description of the context: Hydrogen production via natural gas steam reforming 1.2. The process Hydrogen can be produced from natural gas, oil or coal. Synthesis gas production is a key step, as it gives access to a wide range of options. Synthesis gas which is formed mainly by a mixture of CO and H2 is obtained either by steam-reforming, in the case of natural gas or by partial oxidation. Steam methane reforming is the most common and least expensive method of producing hydrogen. About half of the world's hydrogen is produced from SMR (Gaudernack, 1998). The process can be used also with other light hydrocarbon feedstocks, such as ethane and naphtha. The process is endothermic and synthesis gas is typically produced in a tubular reformer furnace. Module 14 – Life Cycle Assessment 14 NAMP PIECE 1. Description of the context: Hydrogen production via natural gas steam reforming Inlet temperatures are within the range 450-650°C and the product gas leaves the reformer at 700-950°C, depending on the applications (Rostrup-Nielsen, 1993). The desulphurized feedstock is mixed with process steam and reacted over a nickel based catalyst contained in high alloy steel tubes. Although the plant requires some stream for the reforming and shift reactions, the highly exothermic reactions results in an excess amount of steam produced by the plant. Due to the high operating temperature in the reformer, the reformer effluent contains about 10-15 vol % CO (dry basis). A high-temperature shift (HTS) operating at an inlet temperature of 343 to 371°C makes possible to convert about 80 to 90% of the CO. This step uses a catalyst which is typically composed of copper oxide-zinc oxide on alumina. A Pressure Swing Adsorption unit (PSA) is used for removing CO and other contaminants present with hydrogen. Module 14 – Life Cycle Assessment 15 NAMP PIECE 1. Description of the context: Hydrogen production via natural gas steam reforming If the CO2 which is present typically at the level of 15-20% has to be recovered, it may be more appropriate to use a specific step for separating CO2 from hydrogen by solvent scrubbing. An amine solvent is typically used for such a separation step. The hydrogen thus obtained, can be exported. Refining is presently the main consumer of hydrogen. It can be used also in a combined cycle for generating electricity. Such a scheme provides therefore an attractive option for producing electricity, without emitting CO2. Synthesis gas produced during the initial step, can also be used for producing liquid hydrocarbon fuels, through Fischer-Tropsch synthesis. Thus, it is possible to transform any fossil fuel or biomass into hydrogen, electricity and liquid fuels. Module 14 – Life Cycle Assessment 16 NAMP PIECE Tier III: Outline 1. 2. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Module 14 – Life Cycle Assessment 17 NAMP PIECE 2. Problem Statement An oil & gas plant seeks to modernize by looking at 3 process options: improving the environmental aspects, improving the performance of some units of production to maximize the hydrogen production and finaly to install a better system of electronic control of the process. Your are the process engineer in this firm. Your boss, the plant manager, wants you to do a study on the the total environmental aspects (quantification and analysis) of producing 48 MMscfd of hydrogen via natural gas steam reforming for the intern study. In recognition of the fact that upstream processes required for the operation of the Steam Methane Reforming (SMR) plant also produce pollutant and consume energy and natural resources. The data colletion and validation have already been done by another engineer. Module 14 – Life Cycle Assessment 18 NAMP PIECE Tier III: Outline 1. 2. 3. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent Module 14 – Life Cycle Assessment 19 NAMP PIECE Tier III: Outline 1. 2. 3. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries Module 14 – Life Cycle Assessment 20 NAMP PIECE 3. Statement of the intent 3.1. System boundaries This LCA should be performed in a cradle-to-grave manner, for this reason, natural gas production and distribution, as well as electricity generation, were included in the system boundaries. The steps associated with obtaining the natural gas feedstock are drilling/extraction, processing, and pipeline transport. The next figure shows the System Boundaries for Hydrogen Production via Natural Gas Steam Reforming. RM E E Raw Raw material material extraction extraction Em RM RM Construction Construction of of equipment equipment Production Production & & distribution distribution of of electricity electricity RM Em E Recycling Recycling Em Production Production & & distribution distribution of of natural natural gas gas -E Hydrogen Hydrogen production production plant plant -RM -Em Natural Natural gas gas boiler boiler x x x x X -Em X E M Module 14 – Life Cycle Assessment RM Em E E = energy Em = emissions M = materials RM = raw materials Landfilling Landfilling Em E Em E RM Em Production Production & & distribution distribution of of natural natural gas gas -E -RM Avoided operations 21 NAMP PIECE 3. Statement of the intent 3.1. System boundaries For this study, the plant life was set at 20 years with 2 years of construction. In year one, the hydrogen plant begins to operate; plant construction takes place in the two years prior to this (years negative two and negative one). In year one the hydrogen plant is assumed to operate only 45% (50% of 90%) of the time due to start-up activities. In years one through 19, normal plant operation occurs, with a 90% capacity factor. During the last year the hydrogen plant is decommissioned. Therefore, the hydrogen plant will be in operation 67.5% (75% of 90%) of the last year. Module 14 – Life Cycle Assessment 22 NAMP PIECE Tier III: Outline 1. 2. 3. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries b. Major assumptions Module 14 – Life Cycle Assessment 23 NAMP PIECE 3. Statement of the intent 3.2. Major assumptions A pretreatment on the natural gas is necessary to avoid emposoinment of the catalysts with the sulphur. The H2S is removed in a hydrogenation reactor and then in a ZnO bed. After pretreatment, the natural gas and 2.6 MPa steam are fed to the steam reformer. The resulting synthesis gas is then fed to high temperature shift (HTS) and LTS reactors where the water gas shift reaction converts 92% of the CO into H2. Hydrogen Plant Block Flow Diagram H2 product slipstream steam Natural Hydrogenation gas feedstock ZnO Bed Catalytic Steam Reforming High Temperature Shift Low Temperature Shift Pressure Swing Adsorption H2 Off-gas Natural gas fuel Module 14 – Life Cycle Assessment 24 NAMP PIECE 3. Statement of the intent The hydrogen is purified (to 99.9% mol.) using a pressure swing adsorption (PSA) unit. The reformer is fueled primarily by the PSA off-gas, but a small amount of natural gas is used to supply the balance of the reformer duty. The PSA off-gas is comprised of CO2 (47.06 mol%), H2 (24.26 mol%), CH4 (19.59 mol%), CO (7.8 mol%), N2 (0.55 mol%), and some water vapor. The steam reforming process produces 4.8 MPa steam. Electricity is purchased from the grid to operate the pumps and compressors. The hydrogen plant energy efficiency is defined as the total energy produced by hydrogen plant divided by the total energy into the plant, determines by the following formula: energy in product hydrogen 4.8 MPa steam energy (ex ported ) natural gas energy electricity 2.6 MPa steam energy (required ) The base case of this analysis assumed that 1.4% of the natural gas that is produced is lost to the atmosphere due to fugitive emissions. Module 14 – Life Cycle Assessment 25 NAMP PIECE Tier III: Outline 1. 2. 3. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries b. Major assumptions c. Data Construction material Requirement Module 14 – Life Cycle Assessment 26 NAMP PIECE 3. Statement of the intent 3.4.1. Construction material requirement: Construction Plant Materials Requirements and pipeline The next table list materials requirements used for the plant in this study. A sensitivity analysis was performed how changing these numbers would affect the results. Hydrogen Plant Material Requirement (Base Case) Material Amount required (Mg) Concrete 9504.6 Steel 3036.4 Aluminum 25.06 Iron 37.12 Module 14 – Life Cycle Assessment 27 NAMP PIECE 3. Statement of the intent To move the natural gas from the oil or gas wells to the hydrogen plant, we use pipelines. Because the main pipeline is shared by many users, only a portion of the material requirement was allocated for the natural gas combined-cycle plant. For this analysis, the total length of pipeline transport for the natural gas combined-cycle plant is assumed to be 425 km, it was sized so that the total pressure drop in the pipe is of 0.05 psi/100 feet (0.001 MPa/100 meters). The pipe has a diameter of 31 inches assuming a wall thickness of 1 inch. The steel used for the pipe construction has a density of 7700 kg/m3. Module 14 – Life Cycle Assessment 28 NAMP PIECE 3. Statement of the intent 3.4.1. Air Emissions due to materials’ construction Air emissions due to the plant construction Air emission Benzene(C6H6) g of emission/Kg of H2 produced 1.4 CO2 1614.3 CO 5.46 CH4 50.3 NO2 6.86 N2O 0.0150 NMHCs 15.08 Particulate 0.504 SO2 6.48 The construction of materials requirements also produce a lot of air emissions. Because of lack of data, we will suppose that those constructions emit 2.8652 ton of particulate/hectare of the mill/month of activity. You can suppose that NMHCs = 50% mass. benzene + 50% mass. Toluene. Module 14 – Life Cycle Assessment 29 NAMP PIECE Tier III: Outline 1. 2. 3. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries b. Major assumptions c. Data Construction material Requirement Natural gas composition and lost Module 14 – Life Cycle Assessment 30 NAMP PIECE 3. Statement of the intent 3.4.2. Natural gas composition and loss While natural gas is generally though of as methane, about 5-25% of the volume is comprised of ethane, propane, butane, hydrogen sulfide, and inerts (nitrogen, CO2 and helium). The relative amounts of these components can vary greatly depending on the location of the wellhead. The next table gives the composition of the natural gas feedstock use in this analysis, as well as typical pipeline and wellhead compositions. The composition used in this study (first column) assumes that the natural gas has undergo a pretreatment before entering the desulphurization reactor. The natural gas feedstock contains up to 7 ppmv total sulfur, max. 5 ppmv in the form of hydrogen sulphide (H2S) and max. 2 ppmv organic sulfur as mercaptane. Module 14 – Life Cycle Assessment 31 NAMP PIECE 3. Statement of the intent Natural Gas Composition Natural gas feedstock used in analysis Component Typical range of wellhead components (mol%) Mol % (dry) Low value High value Methane (CH4) 83.59 75 99 Ethane (C2H6) 10.19 1 15 Propane (C3H8) 1.15 1 10 Nitrogen (N2) 1.00 0 15 Carbon Dioxide (CO2) 0.78 0 10 Iso-butane (C4H10) 0.11 0 1 N-butane (C4H10) 0.17 0 2 Pentanes (C5+) 0.04 0 1 N-pentane 0.03 0 ---- N- +(C6) 0.03 0 ---- Hydrogen (H2) 2.91 0 ---- Module 14 – Life Cycle Assessment 32 NAMP PIECE 3. Statement of the intent In extracting, process, transmitting, storing and distributing natural gas, some is lost to the atmosphere. Over the past two decades, the natural gas industry and others have tried to better quantify the losses. There is a general consensus that fugitive emissions are the largest source, accounting for about 38% of the total, and that nearly 90% of the fugitive emissions are a result of leaking compressor components. The second largest source of methane emissions comes from pneumatic control devices, accounting for approximately 20% of the total losses. The majority of the pneumatic losses happen during the extraction step. Engine exhaust is the third largest source of methane emissions due to incomplete combustion in reciprocating engines and turbines used in moving the natural gas through the pipeline. These three sources make up nearly 75 % of the overall estimated methane emissions. The remaining 25% come from sources such as dehydrators, purging of transmissions/storage equipment, and meter and pressure regulating stations in distribution lines. Module 14 – Life Cycle Assessment 33 NAMP PIECE Tier III: Outline 1. Description of the context: Hydrogen production via natural gas steam reforming 2. Problem statement 3. Statement of the intent a. System boundaries b. Major assumptions c. Data Construction material Requirement Natural gas composition and lost Production and distribution of electricity Module 14 – Life Cycle Assessment 34 NAMP PIECE 3. Statement of the intent 3.4.3. production and distribution of electricity Electricity is purchased from the grid to operate the pumps and compressors. The production was assumed to be the generation mix of coal, lignite (hard coal), oil and fuel/natural gas. The process consume approx. 129,104 Mj/day. Each fuel provide respectively 3%, 2%, 72% and 23% of the total energy needed by the process. The stressors associated with this mix should also determined in a cradle-to-grave manner. The table below presents the quantity (in kg) of air emissions for each fossil fuel used for electricity production. Those data relate to a functional unit of 1 Tj net electricity delivered from the power plant. Coal Fuel gas Oil Lignite CO2 275833 245831 229380 370979 CO 56.6 81.97 75.15 45.1 NOx 451.7 408.44 488 12.6 SO2 1062.07 58.29 2359.4 3623.53 Particulates 321.59 16.13 96.87 257.66 N2O 1.79 1.5 5.53 1.8 Module 14 – Life Cycle Assessment 35 NAMP PIECE Tier III: Outline 1. 2. 3. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries b. Major assumptions c. Data Construction material Requirement Natural gas composition and lost Production and distribution of electricity H2 Production plant Module 14 – Life Cycle Assessment 36 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant Hydrogenation and Desulphurization As the reformer catalyst is sensitive to poisoning from sulfur, sulfur in the natural gasis processed in a Hydrogenation Reactor. Sulfur is totaly converted to hydrogen sulfide in this Hydrogenation reactor and will be absorbed on the zinc oxide by conversion of ZnO to ZnS in the desulphurization reactor. Natural gas leaving the reactor will have a residual sulfur content of less than 0.2 ppmv. The total adsorption capacity of the desulphurization catalyst, based on total 7 ppmv sulfur in the feedstock will be for minimum 2 years of uninterrupted operation. A small amount of hydrogen, which is recycled from the product stream, is used in the Hydrogenation step to adjust the pressure in the reactor. The table below gives the caractheristics of the inflow of the hydrogenation reactor. Inflows to the hydrogenation reactor The flow in Natural gas feedstock Hydrogen (H2) Module 14 – Life Cycle Assessment Kg/h Kmol/h 17222 962 57 28 37 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant Steam reforming In the steam reforming, the mixture of desulphurized natural gas and process steam (3358 kmol/h at 2.6 MPa (380 psi)) is reformed under application or external heat. The principle chemical reactions taking place in the steam reformer are as follows: Steam reforming Cn H m nH 2O nCO (n m / 2) H 2 heat Water-gas Shift reaction (which is highly exothermic) CO H 2O CO2 H 2 heat The effluent contains besides the products CO2 and residual CH4 and H2O. The reformed gas leaves the SR at 810ºC and approx. 25 kg/cm2 abs.. All reactions take place simultaneously at about 560ºC. However, the reaction as a whole is endothermic. Those reactions take place over a nickel-based catalyst. The waste heat contained in the furnace flue gas is utilized for superheating of the reformer feedstock, generating of medium pressure steam, superheating of the medium pressure steam and preheating of the combustion air. Those gases leave the reformer at approx. 1000ºC. Module 14 – Life Cycle Assessment 38 NAMP PIECE 3. Statement of the intent The reformed gas composition Module 14 – Life Cycle Assessment Components % mol. CO2 6.2 H2 43.73 N2 0.16 C1 4.75 C2 0 C3 0 i-C4 0 N-C4 0 i-C5 0 N-C5 0 N-C6 0 H2O 38.07 CO 7.08 39 NAMP PIECE 3. Statement of the intent The combustion air given is based on 5% excess air and enters the burner at 380ºC and approx. 1.2 kg/cm2, at a rate of 123488 kg/h. It is composed of 20.4% mol. O2, 76.77% mol. N2 and 2.83% of H2O. Waste heat is recovered from the flue gas as well as from the reformed gas to preheat and superheat process streams and for steam production. The natural gas utilized as fuel for the burner contains 5 ppmv of H2S and 2 ppmv of mercaptane and has the following composition and characteristics: Molar mass (kg/mol) 18.38 Flow in kmol/h 26.4 Pression (kg/cm2) 2 Temperature (ºC) 20 Module 14 – Life Cycle Assessment 40 NAMP PIECE 3. Statement of the intent Molar composition of of the natural gas used in the burner Components % mol. CO2 0.8 N2 1.02 C1 86.1 C2 10.5 C3 1.18 i-C4 0.11 N-C4 0.17 i-C5 0.04 N-C5 0.04 N-C6 0.04 Module 14 – Life Cycle Assessment The table below presents the composition of the flue gas at the outlet of the burners. Components % mol. CO2 19.28 O2 1.05 N2 60.28 H2O 19.38 41 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant High Temperature Shift (HTS) The carbon monoxide, which is produced in the steam reformer, is converted by means of water vapor on a catalyst in a HTS reactor to hydrogen and carbon dioxide, according to the following reaction: CO H 2O CO2 H 2 heat This reaction is highly exothermic, which leads to temperature rise of about 50ºC. The CO-content at the outlet of the Shift reactor is less than 2 mol-%. Subsequently the shifted gas is cooled down in different exchangers to approx. 36ºC. Process condensate is separated in multiple liquid-gas separators. The gas is then routed to the PSA Unit. Module 14 – Life Cycle Assessment 42 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant Separators The outflow gas from the HTS passes by different exchangers and liquid-gas separators. At the outlet of the last separator, we obtain two flows. On flow of 481 kg/h of liquid water at 35ºC and a gaseous flow principally composed of hydrogen (H2) and carbon dioxide (CO2) at a rate of 43186 kg/h (3945 kmol/h). The table bellow gives the molar composition of this gaseous flow: Molar composition of the gaseous outflow of the last separator before the PSA unit Component Module 14 – Life Cycle Assessment % mol. CO2 16.92 CO 2.8 H2 72.7 H2O 0.27 N2 0.24 CH4 7.07 43 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant Pressure Swing absorption (PSA) For final purification a Pressure Swing Adsorption process is used. The reminder of undesired components are removed from the bulk of hydrogen by means of adsorption on molecular sieves using a PSA. The purification of hydrogen is based on selective adsorption of gas components such as CH4, CO, CO2, N2 and H2O. Hydrogen does not absorb and leaves the PSA unit as a product gas with high purity. Subsequently the pure hydrogen product is compressed and a small amount is recycled to upstream of the Hydrogenation Reactor. The adsorbed gases in the PSA are released and routed as off-gases to the off gas which ensures a stable and constant supply of fuel gas to the burners of the reformer. The Hydrogen (H2) obtained from the PSA has a 99% molar purity. It leaves the PSA Unit at 40ºC at 5149 kg/h (2525 kmol/h). Module 14 – Life Cycle Assessment 44 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant Steam Generation System Waste heat from the process is utilized for steam generation. As the main source of energy, the sensible heat of the reformed gas downstream Steam Reformer is used for steam production in Reformed Gas Waste Heat Boiler. An other source of heat for steam generation is the waste heat of the flue gas leaving the steam reformer. Here additional steam is produced in Flue Gas Waste Heat Boiler. Module 14 – Life Cycle Assessment 45 NAMP PIECE 3. Statement of the intent 3.4.4. H2 Production plant Shut down The process is shuted down for 24 hours every 2 years to change the catalysts. During start-up of the process or PSA Unit failure, we use a burners’ fuel (for the SR) composed in majority of natural gas (12.88 the mole rate of the natural gas used in normal operation case) completed with Raffinery fuel. The mole ratio of thoses two fuels is 8.5. Module 14 – Life Cycle Assessment 46 NAMP PIECE Tier III: Outline 1. 2. 3. 4. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries b. Major assumptions c. Data Report structure Module 14 – Life Cycle Assessment 47 NAMP PIECE 4. Report structure 4.1. Questions for discussion 1- Quantify the environmental loads - resource use and pollutant air emissions - of the system. 2- Make the results more environmentally relevant by translating the emissions using environmental themes method. Identify and evaluate the environmental impacts of the process by making an impact assessment by calculating the total impact. The index list is in the Index towards the end of the problem. Module 14 – Life Cycle Assessment 48 NAMP PIECE 4. Report structure 4.1. Questions for discussion 3- Make a sensitivity study and identify the most important parameters toward their influence on the results of this study. 4- Examine the net emission of greenhouse gases, as well as the major environmental consequences. 5- Substitutions scenarios: What possible improvements on the system could we do ? 7- Make a cost-benefit Analysis, typically involves an economic ROI study. 8- Since Risk is another matter not dealt with in LCA, we won’t ask you about it but you should write a short paragraph about the Ecological Risk Assessment (ERA) related to this process. Module 14 – Life Cycle Assessment 49 NAMP PIECE 4. Report structure 4.2. Suggestion for Report Table of Contents 1. 2. 3. 4. 5. 6. 7. 8. Executive summury Introduction Objectives Summury of results Sensitivity Analysis Impact Assessment Impovement Opportunities Conclusions Module 14 – Life Cycle Assessment 50 NAMP PIECE Tier III: Outline 1. 2. 3. 4. 5. Description of the context: Hydrogen production via natural gas steam reforming Problem statement Statement of the intent a. System boundaries b. Major assumptions c. Data Report structure Recommendations Module 14 – Life Cycle Assessment 51 NAMP PIECE 5. Recommendations 1. When reporting the final results of your work it is important to thoroughly describe the methodology used in this analysis. The report should explicitly define the system analyzed and the boundaries that were set. 2. All assumptions or decisions made in performing the work should be clearly explained and reported along side the final results of this project. 3. The results should not be oversimplified solely for the purposes of presentation. 4. All the environnemental data needed to do this work are given towards the end of the problem (in the Index). 5. You should respect the international standards for LCA (ISO 1404014043) when performing the different steps of the analyze. Module 14 – Life Cycle Assessment 52 NAMP PIECE End of Tier III • • This is the end of Module 14. Please submit your report to your professor for grading. We are always interested in suggestions on how to improve the course. You may contact us at www.namppimodule.org Module 14 – Life Cycle Assessment 53 NAMP PIECE INDEX Module 14 – Life Cycle Assessment 54 NAMP PIECE Impact Categories To meet the needs of this study, categorization and less-is-better approaches have been taken. The next table summarizes the stressors categories and main stressors from the natural gas steam reforming, hydrogen production system. 1. Depletion of abiotic resources Depletion equivalents for abiotic resources, expressed relative to antimony (Sb) and based on ultimate reserves. Substance Static reserve life (years) Natural gas 0.0187 kg Sbeq/m3. Hard coal 0.0134 kg Sbeq/kg Soft coal 0.00671 kg Sbeq/kg Fossil energy 4.81 x 10-4 kg Sbeq/Mj Module 14 – Life Cycle Assessment 55 NAMP PIECE Impact Categories 2. Global warming Global warning potentials for 100 years expressed in relative to CO2 Trace gas GWP 100 years (kg CO2 eqv/kg) CO2 1 CH4 25 N2O 310 NO2 320 3. Acidification Generic acidification equivalents expressed relative to SO2 (CML/NOH 1992; in CML 2002) Module 14 – Life Cycle Assessment Substance AP (g SO2 eqv/g) SO2 1 NOx 0.7 56 NAMP PIECE Impact Categories 4. Photochemical ozone creation potential (contribution to smog) Photochemical ozone creation potentials (POCPs) for high NOx background concentrations expressed relative to ethylene (CML 2002) Module 14 – Life Cycle Assessment Substance High NOx POCPs (kg ethylene/kg) CO 0.027 NO2 0.028 Methane 0.006 Ethane 0.123 Propane 0.176 N-butane 0.352 N-pentane 0.395 N-C6 0.495 Benzene 0.218 Toluene 0.637 57 NAMP PIECE Impact Categories 5. Human toxicity Human toxicity potentiels, HTPinf, for infinite horizon and global scale. The indicators are expressed relative to 1,4-dichlorobenzene Substance HTP for emissions to air NO2 1.2 SO2 0.096 Benzene 1900 Toluene 0.33 6. Eutrophication Generic eutrophication equivalents for emissions to air, water and soil. Indicators are expressed relative to PO3-4 (CML/NOH 1992; CML 2002). Module 14 – Life Cycle Assessment Substance (g PO3-4 /g) PO3-4 1 H3 PO4 0.97 P 3.06 NH3 0.35 NH4+ 0.33 N 0.42 58 NAMP PIECE Impacts Associated with Stressor Categories Impact Categories Major Impact category H=human health E=ecological health Area impacted L=local (country) R=regional (state) G=global NO H, E R, G CO2, CH4, N2O, CO and NOx (indirectly), water vapor H, E R, G H, E L, R NOx, VOCs H, E L, R Acidification precursors SO2, NOx, CO2 H, E L, R Contributors to corrosion SO2, H2S, H2O E L Other stressors with toxic effects NMHCs, benzene H, E L Resource depletion Fossil fuels, water, minerals and ores E R, G Solid waste Catalysts, coal ash (indirectly), flue gas clean up waste (indirectly) H, E L, R Stressors categories Stressors Major Minor Ozone depletion compounds Greenhouse Gases Climate change Particulates Contributors to smog Photoquemical Module 14 – Life Cycle Assessment 59 NAMP PIECE Economic data Catalysts The reactor The catalyst Desulphurisation reactor Zinc Oxide Desulphurisation Catalyst (ZnODs) SR Description Quantity (m3) Price Zinc Oxide based catalyst having specific physical and textural properties blended with suitable binders in the form of pellets 16.5 3.5 US/lb Nickel Based A nickel based catalyst on alpha alumina carrier or calcium aluminate compound in the form of rings/high geometric surface rings. 23.6 3.237 US/L HTS Copper Oxide-Zinc Oxide on Alumina An iron chrome and copper promoted iron chrome based catalyst. 36.5 5.198 US/L Hydrogenation reactor --------------------- 7.2 ----- --------------------- Due to lack of data, we suppose that all these catalysts have the same density than water. Module 14 – Life Cycle Assessment 60 NAMP PIECE Economic data Equipment Equipment Description/Utility Quantity Vessel For water 1 Compressor Centrifugal; Emotor; Isentropic; Combustion Air Fan 3 Compressor Centrifugal; Emotor; Isentropic; Flue gas Fan 2 Compressor H2 compressor, Reciprocating, Isentropic 2 Drum Steam condensate 1 Drum Tank and deaerator 1 Drum For flare gas 1 Drum Gas separator 1 Drum Shifted gas separator 1 Drum Shifted gas separator 1 Drum For fuel gas 1 Shell- tube HE Feed preheater 1 Module 14 – Life Cycle Assessment 61 NAMP PIECE Economic data Shell- tube HE BFW-Preheater 1 Shell- tube HE Reformed gas final cooler 1 Plate HE Blow down cooler 1 Air Cooler Reformed gas air cooler 1 Static Mixer At the feed 1 Pumps Centrifugal; team turbine 2 Pumps Flare condensate; Drum pump 2 Reactor Hydrogenation with jacket 1 Reactor Desulphurization, jacket 1 Reactor HTS 1 Steamturbine For BFW pump; back-pressure turbine 1 Steamturbine Turbine for Fluegas Fan; back-pressure turbine 2 TOTAL 25 Also consider that you need 3 feeds for the alimentation and the effluents and that you have 2 purges. Consider also that we use a Straightline depreciation during 10 years with a resale price of 0$. Module 14 – Life Cycle Assessment 62 NAMP PIECE Economic data H2 price Gray and Tomlinson (2000) proposed equations to calculate the hydrogen costs based on the prices of fuels in the world-wide market, in these equations it is assumed that the value of hydrogen is equal to the cost of producing it from reformation. Based on this the cost of sale of hydrogen is given by: Where: CSH = 0.45•CGN + 0.76 CSH = Cost of Hydrogen Duty ($/MPCSD) CGN = Cost of Natural Gas ($/MMBtu) Gray y Tomlinson (2000) also established a simple equation to estimate the cost of the natural gas in function of the price of petroleum in the world, which is: Where: CGN = 0.13•PPM PPM = Price of the Petrol in the World ($/BBL) Most of the hydrogen produced at the present time is consumed in its site of production. When it is sold in the market, to its production cost is added the cost of liquefying it and of transporting it. Module 14 – Life Cycle Assessment 63 NAMP PIECE Economic data Electricity cost In order to calculate the cost of the electricity used to produce hydrogen, Gray and Tomlinson (2000) assumed that the value of the electricity is determined by the cost of producing it with a advanced plant of combined cycle of natural gas. It was assumed that the cost of capital of this type of plants is of $494/kw and an amount of specified energy of 6.396 BTU/KW. Based on these estimations the sale price required of the electricity it is given by the following equation: Where: CEPH = 0.0064•CGN + 0.0116 CEPH = Cost of electricity for produce hydrogen ($/KWh) ...the end. Module 14 – Life Cycle Assessment 64