The document provides guidance on developing carbon capture and storage (CCS) emission estimation methodologies for national greenhouse gas inventories. It outlines that CCS involves capturing CO2 at industrial facilities, transporting it via pipelines or ships, and injecting it into geological storage sites for long-term isolation. Emissions should be reported by country based on where capture, transport, injection and storage occur to provide a complete national estimate. Default emission factors are given for different components of CCS systems to support tier 1 methodology estimates.
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2Global CCS Institute
This document outlines a life cycle assessment of CO2 emissions from a CO2-EOR project in southern Mexico. It describes the goal of understanding environmental impacts from a life cycle perspective and estimating CO2 emissions associated with various steps of the project. The methodology estimates emissions using activity data and emission factors. Results found that CO2 emissions from the offshore platform to refinery via the EOR project were 5.41 tCO2eq per ton of CO2 injected, and the project reduced greenhouse gas emissions and environmental impacts compared to business as usual.
IRJET- Capturing carbon dioxide from air by using Sodium hydroxide (CO2 T...IRJET Journal
This document describes a method for capturing carbon dioxide from air using sodium hydroxide (NaOH). The authors designed and tested a prototype air purifier that uses a mist of NaOH solution to absorb CO2 from ambient air as it passes through a filtration structure. CO2 reacts with NaOH to form sodium carbonate, which is then reacted with calcium hydroxide to regenerate the NaOH solution. Experimental results show removal efficiencies up to 63% for air with 4% CO2 concentration when using a 3% NaOH solution at 100°C. Higher NaOH concentrations and temperatures increased CO2 absorption. The system aims to directly capture CO2 from the air as a way to reduce greenhouse gas levels in a
This document discusses the development of an improved greenhouse gas inventory for UK agriculture. It outlines several activities across three projects aimed at better quantifying agricultural emissions:
1) Prioritizing measurement and data collection based on key uncertainties and knowledge gaps.
2) Gathering farm practice data and developing proxies to estimate emissions where direct measurement is not possible.
3) Conducting experiments to generate country-specific emission factors for methane from livestock and nitrous oxide from soils.
4) Standardizing measurement protocols and engaging in training and knowledge exchange between researchers.
The overall goal is to create an inventory tool that more accurately represents UK agricultural conditions and emissions over time to monitor progress towards emissions targets.
Avoid Air-rors! Discuss the Air Regulations that Impact Oil and Gas DevelopmentTrihydro Corporation
Presentation about the air regulations affecting oil and gas development. Topics covered include NSPS OOOO, Leak Detection and Repair, Greenhouse Gas Inventory/Reporting, Optical Gas Imaging with Infrared Cameras
The CoCO2 project aims to develop prototype systems for monitoring and verifying European anthropogenic CO2 emissions using the CO2M model implemented within Copernicus. The Integrated Forecasting System global prototype uses optimized surface fluxes and uncertainties from observations like TROPOMI against prior information from a forward model. Updates to model components like using CB05-BASCOE for the CH4 chemical sink and CMEMS ocean fluxes improve fits to observations. However, errors in land auxiliary data like leaf area index remain a key source of uncertainty in the CO2 sink that the IFS inversion is working to correct.
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2Global CCS Institute
This document outlines a life cycle assessment of CO2 emissions from a CO2-EOR project in southern Mexico. It describes the goal of understanding environmental impacts from a life cycle perspective and estimating CO2 emissions associated with various steps of the project. The methodology estimates emissions using activity data and emission factors. Results found that CO2 emissions from the offshore platform to refinery via the EOR project were 5.41 tCO2eq per ton of CO2 injected, and the project reduced greenhouse gas emissions and environmental impacts compared to business as usual.
IRJET- Capturing carbon dioxide from air by using Sodium hydroxide (CO2 T...IRJET Journal
This document describes a method for capturing carbon dioxide from air using sodium hydroxide (NaOH). The authors designed and tested a prototype air purifier that uses a mist of NaOH solution to absorb CO2 from ambient air as it passes through a filtration structure. CO2 reacts with NaOH to form sodium carbonate, which is then reacted with calcium hydroxide to regenerate the NaOH solution. Experimental results show removal efficiencies up to 63% for air with 4% CO2 concentration when using a 3% NaOH solution at 100°C. Higher NaOH concentrations and temperatures increased CO2 absorption. The system aims to directly capture CO2 from the air as a way to reduce greenhouse gas levels in a
This document discusses the development of an improved greenhouse gas inventory for UK agriculture. It outlines several activities across three projects aimed at better quantifying agricultural emissions:
1) Prioritizing measurement and data collection based on key uncertainties and knowledge gaps.
2) Gathering farm practice data and developing proxies to estimate emissions where direct measurement is not possible.
3) Conducting experiments to generate country-specific emission factors for methane from livestock and nitrous oxide from soils.
4) Standardizing measurement protocols and engaging in training and knowledge exchange between researchers.
The overall goal is to create an inventory tool that more accurately represents UK agricultural conditions and emissions over time to monitor progress towards emissions targets.
Avoid Air-rors! Discuss the Air Regulations that Impact Oil and Gas DevelopmentTrihydro Corporation
Presentation about the air regulations affecting oil and gas development. Topics covered include NSPS OOOO, Leak Detection and Repair, Greenhouse Gas Inventory/Reporting, Optical Gas Imaging with Infrared Cameras
The CoCO2 project aims to develop prototype systems for monitoring and verifying European anthropogenic CO2 emissions using the CO2M model implemented within Copernicus. The Integrated Forecasting System global prototype uses optimized surface fluxes and uncertainties from observations like TROPOMI against prior information from a forward model. Updates to model components like using CB05-BASCOE for the CH4 chemical sink and CMEMS ocean fluxes improve fits to observations. However, errors in land auxiliary data like leaf area index remain a key source of uncertainty in the CO2 sink that the IFS inversion is working to correct.
The document discusses the need to control CO2 emissions and various methods for doing so. It explains that CO2 and other greenhouse gases trap heat in the atmosphere and are causing global climate change. It then outlines different technologies for capturing CO2 from power plants, such as solvent absorption and membrane separation. Finally, it discusses options for storing captured CO2 underground or in the oceans and shifting to non-fossil energy sources like solar, wind and geothermal to reduce CO2 emissions.
Increasing interest by governments worldwide on reducing CO2 released into the atmosphere form a nexus of of opportunity with enhanced oil recovery which could benefit mature oil fields in nearly every country. Overall approximately two-thirds of original oil in place (OOIP) in mature conventional oil fields remains after primary or primary/secondary recovery efforts have taken place. CO2 enhanced oil recovery (CO2 EOR) has an excellent record of revitalizing these mature plays and can dramatically increase ultimate recovery. Since the first CO2 EOR project was initiated in 1972, more than 154 additional projects have been put into operation around the world and about two-thirds are located in the Permian basin and Gulf coast regions of the United States. While these regions have favorable geologic and reservoir conditions for CO2 EOR, they are also located near large natural sources of CO2.
In recent years an increasing number of projects have been developed in areas without natural supplies, and have instead utilized captured CO2 from a variety of anthropogenic sources including gas processing plants, ethanol plants, cement plants, and fertilizer plants. Today approximately 36% of active CO2 EOR projects utilize gas that would otherwise be vented to the atmosphere. Interest world-wide has increased, including projects in Canada, Brazil, Norway, Turkey, Trinidad, and more recently, and perhaps most significantly, in Saudi Arabia and Qatar. About 80% of all energy used in the world comes from fossil fuels, and many industrial and manufacturing processes generate CO2 that can be captured and used for EOR. In this 30 minute presentation a brief history of CO2 EOR is provided, implications for utilizing captured carbon are discussed, and a demonstration project is introduced with an overview of characterization, modeling, simulation, and monitoring actvities taking place during injection of more than a million metric tons (~19 Bcf) of anthropogenic CO2 into a mature waterflood.
Longer versions of the presentation can be requested and can cover details of geologic and seimic characterization, simulation studies, time-lapse monitoring, tracer studies, or other CO2 monitoring technologies.
The Role of Carbon Capture Storage (CCS) and Carbon Capture Utilization (CCU)...Ofori Kwabena
The role of Carbon Capture and Storage & Carbon Capture and Utilization-
Capturing carbon dioxide and storing (CCS) is a climate change mitigation technology which is aimed at reducing CO2 emissions. The utilization of CO2 (CCU) in the manufacture of commercial products is also a technology used to complement CCS technology.
This paper presents a literature review on the mechanisms, developments, cost analysis, life cycle environmental impacts, challenges and policy options that are associated with these technologies.
This document discusses hydrogen production via steam reforming with CO2 capture. It examines the possibilities of capturing CO2 from a steam reforming hydrogen plant. There are three main locations where CO2 can be captured: 1) from the raw hydrogen stream before purification, 2) from the purge gas stream after purification, and 3) from the steam reformer flue gas. Capturing from the raw hydrogen and flue gas streams can achieve overall CO2 removal rates of 60% and 90%, respectively. Amine-based capture is commonly used for the raw hydrogen and flue gas streams. A case study found the cost of capturing from the flue gas to be higher than from the raw hydrogen stream, and in both cases the
Carbon Sequestration Final Proposal (LINKEDIN)Alex Rojas
This report proposes a design to capture and store carbon dioxide emissions from Cornell University's power plant. The major components are a water spray cooler to lower the temperature of flue gas from the plant, a series of MEA columns to separate CO2 from the flue gas, and a pipeline to transport CO2 16.5 miles to a storage site near another power plant. The total estimated cost is $80 million to capture 65,000 lbs/hr of CO2, and the project would take 5.5 years to construct with storage lasting 125 years. Risks like pipeline failures and groundwater displacement are also analyzed.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current science, large-scale demonstration projects are still needed to reduce costs and prove safety and effectiveness. If a policy framework creates incentives to reduce carbon emissions, carbon capture and storage at the scale of the oil and gas industry could cost around $1 trillion annually but help achieve climate goals.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current knowledge, large-scale implementation faces challenges of high costs estimated at $1 trillion per year globally, an incomplete legal framework, and open questions about safety and permanent storage that require further study. Pilot projects demonstrate the technical feasibility of capturing CO2 and storing it underground, like the Sleipner gas field in Norway that has stored over 1 million tons of CO2 annually since 1996.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current knowledge, large-scale implementation faces challenges of high costs estimated at $1 trillion per year globally, an incomplete legal framework, and open questions about safety and permanent storage that require further study. Pilot projects demonstrate the technical feasibility of capturing CO2 and storing it underground, like the Sleipner gas field in Norway that has stored over 1 million tons of CO2 annually since 1996.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current knowledge, large-scale implementation faces challenges of high costs estimated at $1 trillion per year globally, an incomplete legal framework, and open questions about safety and permanent storage that require further study. Pilot projects demonstrate the technical feasibility of capturing CO2 and storing it underground, like the Sleipner gas field in Norway that has stored over 1 million tons of CO2 annually since 1996.
This document discusses improving atmospheric measurements on Ships of Opportunity (SOOP) as part of the Ringo Task 3.2 project. Three SOOP lines - SOOP Tavastland, SOOP Colibri, and SOOP Atlantic Sail - are being equipped with instrumentation to measure atmospheric CO2, CH4, and other greenhouse gases to standards matching the ICOS Atmospheric Thematic Centre. Initial results from SOOP Colibri show data quality matching these standards and capturing gradients and variability not seen in models. Next steps include finalizing the setup on SOOP Tavastland and assessing the added value of these new SOOP measurements for inverse modeling.
This document discusses carbon dioxide (CO2) capture from power plant flue gases. It begins by outlining the need to reduce CO2 emissions due to constraints on emissions and fossil fuel resources. It then discusses various CO2 capture technologies currently used or under development for post-combustion, pre-combustion, and oxy-fuel combustion processes. These include chemical absorption, adsorption, membranes, and cryogenic separation. The document also addresses the costs, challenges, and energy penalties associated with implementing CO2 capture at power plants.
Burr mach - georgeson air emissions modeling advances - to gpazubeditufail
This document discusses advances in modeling air emissions from oil and gas production facilities. It describes how process simulation software can now automatically calculate volatile organic compound (VOC) emissions over a range of conditions, making compliance with regulations more efficient. Traditionally, emissions were calculated individually for each facility using standard methods. New tools allow modeling entire production networks and optimizing designs to reduce emissions.
Power Generation in Future by Using Landfill GasesIJARIIT
this paper describes an approach to power generation in future by using landfill gases. The present day methods of power generation are not much efficient & it may not be sufficient or suitable to keep pace with ever increasing demand. The recent severe energy crisis has forced the world to rethink & develop the landfill gas type power generation which remained unthinkable for several years after its discovery. Generation of electricity by using landfill gases is unique and highly efficient with nearly zero pollution. Landfill gas utilization is a process of gathering, processing, and treating the methane gas emitted from decomposing garbage to produce electricity. In advanced countries this technique is already in use but in developing countries it’s still under construction. The efficiency is also better than other non-conventional energy sources. These projects are popular because they control energy costs and reduce greenhouse gas emissions. These projects collect the methane gas and treat it, so it can be used for electricity or upgraded to pipeline-grade gas. These projects power homes, buildings, and vehicles. Keywords-landfill gas process, LFG collection system, flaring, LFG gas treatment, gas turbine, and micro turbine.
CO2 Capture Using Ti-MOFs in an Arduino-Controlled Artificial Tree.pdfShruthiPrakash18
Led Ti-MOF integration for efficient CO2 adsorption, designed sustainable structures, ensured environmental compliance, fostered collaboration for increased throughput, and enhanced project efficiency through root cause analysis.
This document provides an overview of carbon capture and storage (CCS) systems. It discusses the need to reduce CO2 emissions to mitigate climate change. CCS systems aim to capture over 80% of CO2 emissions from power plants and industrial facilities, transport it via pipelines or ships, and store it underground in geological formations or in the deep ocean. The document describes different capture methods including pre-combustion, post-combustion, and oxyfuel combustion. It also discusses transportation and storage options as well as some real-world CCS project sites. While CCS could significantly reduce emissions, the technology is currently very expensive and poses risks if CO2 leaks from storage locations. More research is still needed to improve C
This document discusses the Society of Petroleum Engineers Distinguished Lecturer Program. It provides the following key details in 3 sentences:
The SPE Distinguished Lecturer Program is funded primarily by the SPE Foundation through member donations and Offshore Europe. It allows industry professionals to serve as lecturers on topics like CO2 storage and CO2-EOR. Additional support is provided by AIME to further the program's educational mission.
Absorption of CO2 gas from CO
2/Air mixture into aqueous sodium hydroxide solution has been
achieved using packed column in pilot scale at constant temperature (T) of 25±1℃.The aim of the present work
was to improve the Absorption rate of this process, to find the optimal operation conditions, and to contribute to
the using of this process in the chemical industry. Absorption rate (RA) was measured by using different
operating parameters: gas mixture flow rate (G) of 360 -540 m3/h, carbon dioxide inlet concentration (CCO
2) of
0.1-0.5 vol. %, NaOH solution concentration (CNaOH) of 1-2 M, and liquid holdup in the column (VL) of 0.022-0.028 m3 according to experimental design. The measured RA was in the range of RA = 3.235 – 22.340 k-mol/h.
Computer program (Statgraphics/Experimental Design) was used to estimate the fitted linear model of RA in
terms of (G, CCO2, CNaOH, and VL), and the economic aspects of the process. R -squared of RA model was
91.7659 percent, while the standard error of the estimate shows the standard deviation of the residuals to be
1.7619. The linear model of RA was adequate, the operating parameters were significant except the liquid holdup
was not significant, and the interactions were negligible.
The document discusses the need to control CO2 emissions and various methods for doing so. It explains that CO2 and other greenhouse gases trap heat in the atmosphere and are causing global climate change. It then outlines different technologies for capturing CO2 from power plants, such as solvent absorption and membrane separation. Finally, it discusses options for storing captured CO2 underground or in the oceans and shifting to non-fossil energy sources like solar, wind and geothermal to reduce CO2 emissions.
Increasing interest by governments worldwide on reducing CO2 released into the atmosphere form a nexus of of opportunity with enhanced oil recovery which could benefit mature oil fields in nearly every country. Overall approximately two-thirds of original oil in place (OOIP) in mature conventional oil fields remains after primary or primary/secondary recovery efforts have taken place. CO2 enhanced oil recovery (CO2 EOR) has an excellent record of revitalizing these mature plays and can dramatically increase ultimate recovery. Since the first CO2 EOR project was initiated in 1972, more than 154 additional projects have been put into operation around the world and about two-thirds are located in the Permian basin and Gulf coast regions of the United States. While these regions have favorable geologic and reservoir conditions for CO2 EOR, they are also located near large natural sources of CO2.
In recent years an increasing number of projects have been developed in areas without natural supplies, and have instead utilized captured CO2 from a variety of anthropogenic sources including gas processing plants, ethanol plants, cement plants, and fertilizer plants. Today approximately 36% of active CO2 EOR projects utilize gas that would otherwise be vented to the atmosphere. Interest world-wide has increased, including projects in Canada, Brazil, Norway, Turkey, Trinidad, and more recently, and perhaps most significantly, in Saudi Arabia and Qatar. About 80% of all energy used in the world comes from fossil fuels, and many industrial and manufacturing processes generate CO2 that can be captured and used for EOR. In this 30 minute presentation a brief history of CO2 EOR is provided, implications for utilizing captured carbon are discussed, and a demonstration project is introduced with an overview of characterization, modeling, simulation, and monitoring actvities taking place during injection of more than a million metric tons (~19 Bcf) of anthropogenic CO2 into a mature waterflood.
Longer versions of the presentation can be requested and can cover details of geologic and seimic characterization, simulation studies, time-lapse monitoring, tracer studies, or other CO2 monitoring technologies.
The Role of Carbon Capture Storage (CCS) and Carbon Capture Utilization (CCU)...Ofori Kwabena
The role of Carbon Capture and Storage & Carbon Capture and Utilization-
Capturing carbon dioxide and storing (CCS) is a climate change mitigation technology which is aimed at reducing CO2 emissions. The utilization of CO2 (CCU) in the manufacture of commercial products is also a technology used to complement CCS technology.
This paper presents a literature review on the mechanisms, developments, cost analysis, life cycle environmental impacts, challenges and policy options that are associated with these technologies.
This document discusses hydrogen production via steam reforming with CO2 capture. It examines the possibilities of capturing CO2 from a steam reforming hydrogen plant. There are three main locations where CO2 can be captured: 1) from the raw hydrogen stream before purification, 2) from the purge gas stream after purification, and 3) from the steam reformer flue gas. Capturing from the raw hydrogen and flue gas streams can achieve overall CO2 removal rates of 60% and 90%, respectively. Amine-based capture is commonly used for the raw hydrogen and flue gas streams. A case study found the cost of capturing from the flue gas to be higher than from the raw hydrogen stream, and in both cases the
Carbon Sequestration Final Proposal (LINKEDIN)Alex Rojas
This report proposes a design to capture and store carbon dioxide emissions from Cornell University's power plant. The major components are a water spray cooler to lower the temperature of flue gas from the plant, a series of MEA columns to separate CO2 from the flue gas, and a pipeline to transport CO2 16.5 miles to a storage site near another power plant. The total estimated cost is $80 million to capture 65,000 lbs/hr of CO2, and the project would take 5.5 years to construct with storage lasting 125 years. Risks like pipeline failures and groundwater displacement are also analyzed.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current science, large-scale demonstration projects are still needed to reduce costs and prove safety and effectiveness. If a policy framework creates incentives to reduce carbon emissions, carbon capture and storage at the scale of the oil and gas industry could cost around $1 trillion annually but help achieve climate goals.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current knowledge, large-scale implementation faces challenges of high costs estimated at $1 trillion per year globally, an incomplete legal framework, and open questions about safety and permanent storage that require further study. Pilot projects demonstrate the technical feasibility of capturing CO2 and storing it underground, like the Sleipner gas field in Norway that has stored over 1 million tons of CO2 annually since 1996.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current knowledge, large-scale implementation faces challenges of high costs estimated at $1 trillion per year globally, an incomplete legal framework, and open questions about safety and permanent storage that require further study. Pilot projects demonstrate the technical feasibility of capturing CO2 and storing it underground, like the Sleipner gas field in Norway that has stored over 1 million tons of CO2 annually since 1996.
Carbon capture and storage has the potential to allow continued use of fossil fuels while mitigating climate change. It involves capturing carbon dioxide emissions from large point sources like power plants, compressing and transporting the CO2 via pipeline, and injecting it into deep geological formations for long-term storage. While the technology is possible with current knowledge, large-scale implementation faces challenges of high costs estimated at $1 trillion per year globally, an incomplete legal framework, and open questions about safety and permanent storage that require further study. Pilot projects demonstrate the technical feasibility of capturing CO2 and storing it underground, like the Sleipner gas field in Norway that has stored over 1 million tons of CO2 annually since 1996.
This document discusses improving atmospheric measurements on Ships of Opportunity (SOOP) as part of the Ringo Task 3.2 project. Three SOOP lines - SOOP Tavastland, SOOP Colibri, and SOOP Atlantic Sail - are being equipped with instrumentation to measure atmospheric CO2, CH4, and other greenhouse gases to standards matching the ICOS Atmospheric Thematic Centre. Initial results from SOOP Colibri show data quality matching these standards and capturing gradients and variability not seen in models. Next steps include finalizing the setup on SOOP Tavastland and assessing the added value of these new SOOP measurements for inverse modeling.
This document discusses carbon dioxide (CO2) capture from power plant flue gases. It begins by outlining the need to reduce CO2 emissions due to constraints on emissions and fossil fuel resources. It then discusses various CO2 capture technologies currently used or under development for post-combustion, pre-combustion, and oxy-fuel combustion processes. These include chemical absorption, adsorption, membranes, and cryogenic separation. The document also addresses the costs, challenges, and energy penalties associated with implementing CO2 capture at power plants.
Burr mach - georgeson air emissions modeling advances - to gpazubeditufail
This document discusses advances in modeling air emissions from oil and gas production facilities. It describes how process simulation software can now automatically calculate volatile organic compound (VOC) emissions over a range of conditions, making compliance with regulations more efficient. Traditionally, emissions were calculated individually for each facility using standard methods. New tools allow modeling entire production networks and optimizing designs to reduce emissions.
Power Generation in Future by Using Landfill GasesIJARIIT
this paper describes an approach to power generation in future by using landfill gases. The present day methods of power generation are not much efficient & it may not be sufficient or suitable to keep pace with ever increasing demand. The recent severe energy crisis has forced the world to rethink & develop the landfill gas type power generation which remained unthinkable for several years after its discovery. Generation of electricity by using landfill gases is unique and highly efficient with nearly zero pollution. Landfill gas utilization is a process of gathering, processing, and treating the methane gas emitted from decomposing garbage to produce electricity. In advanced countries this technique is already in use but in developing countries it’s still under construction. The efficiency is also better than other non-conventional energy sources. These projects are popular because they control energy costs and reduce greenhouse gas emissions. These projects collect the methane gas and treat it, so it can be used for electricity or upgraded to pipeline-grade gas. These projects power homes, buildings, and vehicles. Keywords-landfill gas process, LFG collection system, flaring, LFG gas treatment, gas turbine, and micro turbine.
CO2 Capture Using Ti-MOFs in an Arduino-Controlled Artificial Tree.pdfShruthiPrakash18
Led Ti-MOF integration for efficient CO2 adsorption, designed sustainable structures, ensured environmental compliance, fostered collaboration for increased throughput, and enhanced project efficiency through root cause analysis.
This document provides an overview of carbon capture and storage (CCS) systems. It discusses the need to reduce CO2 emissions to mitigate climate change. CCS systems aim to capture over 80% of CO2 emissions from power plants and industrial facilities, transport it via pipelines or ships, and store it underground in geological formations or in the deep ocean. The document describes different capture methods including pre-combustion, post-combustion, and oxyfuel combustion. It also discusses transportation and storage options as well as some real-world CCS project sites. While CCS could significantly reduce emissions, the technology is currently very expensive and poses risks if CO2 leaks from storage locations. More research is still needed to improve C
This document discusses the Society of Petroleum Engineers Distinguished Lecturer Program. It provides the following key details in 3 sentences:
The SPE Distinguished Lecturer Program is funded primarily by the SPE Foundation through member donations and Offshore Europe. It allows industry professionals to serve as lecturers on topics like CO2 storage and CO2-EOR. Additional support is provided by AIME to further the program's educational mission.
Absorption of CO2 gas from CO
2/Air mixture into aqueous sodium hydroxide solution has been
achieved using packed column in pilot scale at constant temperature (T) of 25±1℃.The aim of the present work
was to improve the Absorption rate of this process, to find the optimal operation conditions, and to contribute to
the using of this process in the chemical industry. Absorption rate (RA) was measured by using different
operating parameters: gas mixture flow rate (G) of 360 -540 m3/h, carbon dioxide inlet concentration (CCO
2) of
0.1-0.5 vol. %, NaOH solution concentration (CNaOH) of 1-2 M, and liquid holdup in the column (VL) of 0.022-0.028 m3 according to experimental design. The measured RA was in the range of RA = 3.235 – 22.340 k-mol/h.
Computer program (Statgraphics/Experimental Design) was used to estimate the fitted linear model of RA in
terms of (G, CCO2, CNaOH, and VL), and the economic aspects of the process. R -squared of RA model was
91.7659 percent, while the standard error of the estimate shows the standard deviation of the residuals to be
1.7619. The linear model of RA was adequate, the operating parameters were significant except the liquid holdup
was not significant, and the interactions were negligible.
Microbial characterisation and identification, and potability of River Kuywa ...Open Access Research Paper
Water contamination is one of the major causes of water borne diseases worldwide. In Kenya, approximately 43% of people lack access to potable water due to human contamination. River Kuywa water is currently experiencing contamination due to human activities. Its water is widely used for domestic, agricultural, industrial and recreational purposes. This study aimed at characterizing bacteria and fungi in river Kuywa water. Water samples were randomly collected from four sites of the river: site A (Matisi), site B (Ngwelo), site C (Nzoia water pump) and site D (Chalicha), during the dry season (January-March 2018) and wet season (April-July 2018) and were transported to Maseno University Microbiology and plant pathology laboratory for analysis. The characterization and identification of bacteria and fungi were carried out using standard microbiological techniques. Nine bacterial genera and three fungi were identified from Kuywa river water. Clostridium spp., Staphylococcus spp., Enterobacter spp., Streptococcus spp., E. coli, Klebsiella spp., Shigella spp., Proteus spp. and Salmonella spp. Fungi were Fusarium oxysporum, Aspergillus flavus complex and Penicillium species. Wet season recorded highest bacterial and fungal counts (6.61-7.66 and 3.83-6.75cfu/ml) respectively. The results indicated that the river Kuywa water is polluted and therefore unsafe for human consumption before treatment. It is therefore recommended that the communities to ensure that they boil water especially for drinking.
Epcon is One of the World's leading Manufacturing Companies.EpconLP
Epcon is One of the World's leading Manufacturing Companies. With over 4000 installations worldwide, EPCON has been pioneering new techniques since 1977 that have become industry standards now. Founded in 1977, Epcon has grown from a one-man operation to a global leader in developing and manufacturing innovative air pollution control technology and industrial heating equipment.
Recycling and Disposal on SWM Raymond Einyu pptxRayLetai1
Increasing urbanization, rural–urban migration, rising standards of living, and rapid development associated with population growth have resulted in increased solid waste generation by industrial, domestic and other activities in Nairobi City. It has been noted in other contexts too that increasing population, changing consumption patterns, economic development, changing income, urbanization and industrialization all contribute to the increased generation of waste.
With the increasing urban population in Kenya, which is estimated to be growing at a rate higher than that of the country’s general population, waste generation and management is already a major challenge. The industrialization and urbanization process in the country, dominated by one major city – Nairobi, which has around four times the population of the next largest urban centre (Mombasa) – has witnessed an exponential increase in the generation of solid waste. It is projected that by 2030, about 50 per cent of the Kenyan population will be urban.
Aim:
A healthy, safe, secure and sustainable solid waste management system fit for a world – class city.
Improve and protect the public health of Nairobi residents and visitors.
Ecological health, diversity and productivity and maximize resource recovery through the participatory approach.
Goals:
Build awareness and capacity for source separation as essential components of sustainable waste management.
Build new environmentally sound infrastructure and systems for safe disposal of residual waste and replacing current dumpsites which should be commissioned.
Current solid waste management situation:
The status.
Solid waste generation rate is at 2240 tones / day
collection efficiently is at about 50%.
Actors i.e. city authorities, CBO’s , private firms and self-disposal
Current SWM Situation in Nairobi City:
Solid waste generation – collection – dumping
Good Practices:
• Separation – recycling – marketing.
• Open dumpsite dandora dump site through public education on source separation of waste, of which the situation can be reversed.
• Nairobi is one of the C40 cities in this respect , various actors in the solid waste management space have adopted a variety of technologies to reduce short lived climate pollutants including source separation , recycling , marketing of the recycled products.
• Through the network, it should expect to benefit from expertise of the different actors in the network in terms of applicable technologies and practices in reducing the short-lived climate pollutants.
Good practices:
Despite the dismal collection of solid waste in Nairobi city, there are practices and activities of informal actors (CBOs, CBO-SACCOs and yard shop operators) and other formal industrial actors on solid waste collection, recycling and waste reduction.
Practices and activities of these actor groups are viewed as innovations with the potential to change the way solid waste is handled.
CHALLENGES:
• Resource Allocation.
ENVIRONMENT~ Renewable Energy Sources and their future prospects.tiwarimanvi3129
This presentation is for us to know that how our Environment need Attention for protection of our natural resources which are depleted day by day that's why we need to take time and shift our attention to renewable energy sources instead of non-renewable sources which are better and Eco-friendly for our environment. these renewable energy sources are so helpful for our planet and for every living organism which depends on environment.
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...Joshua Orris
Results of geophysics and pneumatic injection pilot tests during 2003 – 2007 yielded significant positive results for injection delivery design and contaminant mass treatment, resulting in permanent shut-down of an existing groundwater Pump & Treat system.
Accessible source areas were subsequently removed (2011) by soil excavation and treated with the placement of Emulsified Vegetable Oil EVO and zero-valent iron ZVI to accelerate treatment of impacted groundwater in overburden and weathered fractured bedrock. Post pilot test and post remediation groundwater monitoring has included analyses of CVOCs, organic fatty acids, dissolved gases and QuantArray® -Chlor to quantify key microorganisms (e.g., Dehalococcoides, Dehalobacter, etc.) and functional genes (e.g., vinyl chloride reductase, methane monooxygenase, etc.) to assess potential for reductive dechlorination and aerobic cometabolism of CVOCs.
In 2022, the first commercial application of MetaArray™ was performed at the site. MetaArray™ utilizes statistical analysis, such as principal component analysis and multivariate analysis to provide evidence that reductive dechlorination is active or even that it is slowing. This creates actionable data allowing users to save money by making important site management decisions earlier.
The results of the MetaArray™ analysis’ support vector machine (SVM) identified groundwater monitoring wells with a 80% confidence that were characterized as either Limited for Reductive Decholorination or had a High Reductive Reduction Dechlorination potential. The results of MetaArray™ will be used to further optimize the site’s post remediation monitoring program for monitored natural attenuation.
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...Open Access Research Paper
Water polluted by dyestuffs compounds is a global threat to health and the environment; accordingly, we prepared a green novel sorbent chemical and Physical system from an algae, chitosan and chitosan nanoparticle and impregnated with algae with chitosan nanocomposite for the sorption of Malachite green dye from water. The algae with chitosan nanocomposite by a simple method and used as a recyclable and effective adsorbent for the removal of malachite green dye from aqueous solutions. Algae, chitosan, chitosan nanoparticle and algae with chitosan nanocomposite were characterized using different physicochemical methods. The functional groups and chemical compounds found in algae, chitosan, chitosan algae, chitosan nanoparticle, and chitosan nanoparticle with algae were identified using FTIR, SEM, and TGADTA/DTG techniques. The optimal adsorption conditions, different dosages, pH and Temperature the amount of algae with chitosan nanocomposite were determined. At optimized conditions and the batch equilibrium studies more than 99% of the dye was removed. The adsorption process data matched well kinetics showed that the reaction order for dye varied with pseudo-first order and pseudo-second order. Furthermore, the maximum adsorption capacity of the algae with chitosan nanocomposite toward malachite green dye reached as high as 15.5mg/g, respectively. Finally, multiple times reusing of algae with chitosan nanocomposite and removing dye from a real wastewater has made it a promising and attractive option for further practical applications.
Improving the viability of probiotics by encapsulation methods for developmen...Open Access Research Paper
The popularity of functional foods among scientists and common people has been increasing day by day. Awareness and modernization make the consumer think better regarding food and nutrition. Now a day’s individual knows very well about the relation between food consumption and disease prevalence. Humans have a diversity of microbes in the gut that together form the gut microflora. Probiotics are the health-promoting live microbial cells improve host health through gut and brain connection and fighting against harmful bacteria. Bifidobacterium and Lactobacillus are the two bacterial genera which are considered to be probiotic. These good bacteria are facing challenges of viability. There are so many factors such as sensitivity to heat, pH, acidity, osmotic effect, mechanical shear, chemical components, freezing and storage time as well which affects the viability of probiotics in the dairy food matrix as well as in the gut. Multiple efforts have been done in the past and ongoing in present for these beneficial microbial population stability until their destination in the gut. One of a useful technique known as microencapsulation makes the probiotic effective in the diversified conditions and maintain these microbe’s community to the optimum level for achieving targeted benefits. Dairy products are found to be an ideal vehicle for probiotic incorporation. It has been seen that the encapsulated microbial cells show higher viability than the free cells in different processing and storage conditions as well as against bile salts in the gut. They make the food functional when incorporated, without affecting the product sensory characteristics.
Presented by The Global Peatlands Assessment: Mapping, Policy, and Action at GLF Peatlands 2024 - The Global Peatlands Assessment: Mapping, Policy, and Action
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...Joshua Orris
The incorporation of a 3DCSM and completion of HRSC provided a tool for enhanced, data-driven, decisions to support a change in remediation closure strategies. Currently, an approved pilot study has been obtained to shut-down the remediation systems (ISCO, P&T) and conduct a hydraulic study under non-pumping conditions. A separate micro-biological bench scale treatability study was competed that yielded positive results for an emerging innovative technology. As a result, a field pilot study has commenced with results expected in nine-twelve months. With the results of the hydraulic study, field pilot studies and an updated risk assessment leading site monitoring optimization cost lifecycle savings upwards of $15MM towards an alternatively evolved best available technology remediation closure strategy.
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
CCS_Inventories_SB24_workshop.ppt
1. INTERGOVERNMENTAL PANEL ON CLIMATE CHANGE
NATIONAL GREENHOUSE GAS INVENTORIES PROGRAMME
WMO UNEP
IPCC Guidance on Developing and
Applying CCS Emission Estimation
Methodologies in National Inventories of
GHGs
Simon Eggleston
3. INTERGOVERNMENTAL
PANEL
ON
CLIMATE
CHANGE
NATIONAL
GREENHOUSE
GAS
INVENTORIES
PROGRAMME
WMO
UNEP
3
Introduction
The 2006 IPCC Guidelines for National
Greenhouse Gas Inventories (2006GL) give a
complete methodology for CCS
Capture treated in the sector it may occur - volumes 2 & 3
Remaining emissions in CCS chapter in - volume 2
This approach is consistent with the IPCC Special
Report on CCS
No “Tier 1” Methods available for storage – this
must be based on site specific evaluation
There are demonstration projects but no wide scale use of
CCS. Some technologies are well known
Use of CO2 pipelines and associated equipment
Modelling and investigation of oil and gas fields
4. INTERGOVERNMENTAL
PANEL
ON
CLIMATE
CHANGE
NATIONAL
GREENHOUSE
GAS
INVENTORIES
PROGRAMME
WMO
UNEP
4
Consistency
The approach adopted is consistent with the
remainder of the 2006 guidelines,
in particular a fundamental principle that the
inventory methods reflect the estimated actual
emissions in the year in which they occur;
emissions are reported where they occur;
and in line with the approach used for the
treatment of biogenic material.
The methods in the 2006 Guidelines are
compatible with the revised 1996 IPCC
guidelines and subsequent good practice
guidance.
5. INTERGOVERNMENTAL
PANEL
ON
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CHANGE
NATIONAL
GREENHOUSE
GAS
INVENTORIES
PROGRAMME
WMO
UNEP
5
Types of Storage
The 2006GLs provide emission estimation
guidance for the capture and transport of CO2 and
for geological storage.
No emissions estimation methods are provided for
any other type of storage option such as ocean
storage or conversion of CO2 into inert inorganic
carbonates.
Geological CO2 storage may take place either at
sites where the sole purpose is CO2 storage,
or in association with enhanced oil recovery (EOR),
enhanced gas recovery (EGR)
enhanced coal-bed methane recovery operations (ECBM)
7. INTERGOVERNMENTAL
PANEL
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GREENHOUSE
GAS
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PROGRAMME
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UNEP
7
Source Categories for CCS
1C Carbon dioxide (CO2) capture and storage (CCS) involves the capture of CO2,
its transport to a storage location and its long-term isolation from the
atmosphere. Emissions associated with CO2 transport, injection and storage
are covered under category 1C. Emissions (and reductions) associated with
CO2 capture should be reported under the IPCC sector in which capture takes
place (e.g. Stationary Combustion or Industrial Activities).
1C1 Transport
of CO2
Fugitive emissions from the systems used to transport captured CO2 from the
source to the injection site. These emissions may comprise fugitive losses due
to equipment leaks, venting and releases due to pipeline ruptures or other
accidental releases.
1C1a Pipelines Fugitive emissions from the pipeline system used to transport CO2
1C1b Ships Fugitive emissions from the ships used to transport CO2
1C1c Other Fugitive emissions from other systems used to transport CO2
1C2 Injection
and
Storage
Fugitive emissions from activities and equipment at the injection site and
those from the end containment once the CO2 is placed in storage.
1C2a Injection Fugitive emissions from activities and equipment at the injection site.
1C2b Storage Fugitive emissions from the end containment once the CO2 is placed in
storage.
1C3 Other Any other emissions from CCS not reported elsewhere
10. INTERGOVERNMENTAL
PANEL
ON
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CHANGE
NATIONAL
GREENHOUSE
GAS
INVENTORIES
PROGRAMME
WMO
UNEP
10
CO2 Transport
Pipelines
Leaks from compressors, temporary storage and other
equipment
Existing CO2 pipelines so experience available
Can also use information from other gas pipelines
Shipping
Leaks from equipment, compressors, liquefiers and
storage
Leaks form ships not well known
Trains and Road
Possible but unlikely given the large quantities likely to be
captured
No methods in the guidelines
13. INTERGOVERNMENTAL
PANEL
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GAS
INVENTORIES
PROGRAMME
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UNEP
13
CO2 Injection
Includes all equipment at well head
storage facilities,
any distribution manifold at the end of the transport pipeline,
distribution pipelines to wells,
additional compression facilities, measurement and control
systems,
wellhead(s) and the injection wells.
Measurements at the wellhead of the injected fluid :
the flow rate,
temperature
pressure.
The composition of the imported CO2 commonly shows little
variation and can be analyzed periodically using a gas
chromatograph.
14. INTERGOVERNMENTAL
PANEL
ON
CLIMATE
CHANGE
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GREENHOUSE
GAS
INVENTORIES
PROGRAMME
WMO
UNEP
14
Storage Sites
Monitoring
Estimating, Verifying & Reporting Emissions from CO2 Storage Sites
Assessment
of
Risk
of
Leakage
Reporting
Site
Characterization
Confirm that geology of storage site has been evaluated and that local and
regional hydrogeology and leakage pathways have been identified.
Confirm that the potential for leakage has been evaluated through a
combination of site characterization and realistic models that predict
movement of CO2 over time and locations where emissions might occur.
Ensure that an adequate monitoring plan is in place. The monitoring plan
should identify potential leakage pathways, measure leakage and/or
validate update models as appropriate.
Report CO2 injected and emissions from storage site
15. INTERGOVERNMENTAL
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GAS
INVENTORIES
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UNEP
15
Potential Emission Pathways from
Geological Reservoirs
Type of emission Potential Emissions Pathways/ Sources
Direct leakage
pathways created by
wells and mining
Operational or abandoned wells
Well blow-outs (uncontrolled emissions from injection wells)
Future mining of CO2 reservoir
Natural leakage and
migration pathways
(that may lead to
emissions over time)
Through the pore system in low permeability cap rocks if the
capillary entry pressure is exceeded or the CO2 is in solution
If the cap rock is locally absent
Via a spill point if reservoir is overfilled
Through a degraded cap rock as a result of CO2/water/rock
reactions
Via dissolution of CO2 into pore fluid and subsequent transport
out of the storage site by natural fluid flow
Via natural or induced faults and/or fractures
Other Fugitive
Emissions at the
Geological Storage
Site
Fugitive methane emissions could result from the displacement
of CH4 by CO2 at geological storage sites. This is particularly
the case for ECBM, EOR, and depleted oil and gas reservoirs.
16. INTERGOVERNMENTAL
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16
Reporting
Complete national reporting includes
CO2 from capture in the country
CO2 leakage from all transport and injection in that country
CO2 leakage from all storage sites in that country
(wherever the CO2 actually reaches the surface).
Imports and exports of captured CO2.
Total CO2 in storage should be reported in the
accompanying documentation
Quantities of CO2 for later use and short-term
storage should not be deducted from CO2
emissions (except in the case of recovery of CO2 for urea production –
see guidelines).
19. INTERGOVERNMENTAL
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Conclusion
The 2006 IPCC Guidelines provide a complete consistent
methodology for CCS that is also compatible with the 1996
Guidelines
This covers capture, transport, injection and geological
storage
Capture and transport have straightforward methods
Storage require detailed site characterisation including
modelling and monitoring
however this is unlikely to be a significant burden as this is likely
to be required for regulatory as well as health and safety
requirements
Need to reconcile capture, storage, imports and exports.