1) The document compares the results of modeling carbon monoxide (CO) concentration levels in Delhi, India for the year 2002 using the air quality models MUAIR2.0, ISC3, and Caline4.
2) It models CO concentrations for different scenarios: area sources only, selected area sources, point sources only, and combined area and point sources. The highest hourly and annual average CO concentrations from each model run are reported.
3) MUAIR2.0 results showed the highest hourly CO concentration was 271.39 mg/m3 at location (12,500, 6,500), while the highest annual average was 78.83 mg/m3 at the same location,
Development of Ammonia Gas Leak Detection and Location MethodTELKOMNIKA JOURNAL
This paper proposed the gas for industrial ammonia leak diffusion model and the Gauss method
of leakage localization. A set of wireless ammonia leak alarm system is composed of sensor node, network
coordinator and host used in the industrial field was developed, the purpose is to reduce the loss of
property caused by the leakage of ammonia industry. Using the monitoring system to carry out the
ammonia leak location simulation measurement experiment, the result shows that the relative positioning
error of the monitoring system is about 12%, which meets the needs of industrial production safety
monitoring. Using the wireless sensor network to monitor the concentration of ammonia gas and locate the
leakage source, it solves the problems of traditional wired alarm system, such as difficult wiring and weak
expansibility, which helps to find the leak timely and provides a reference for the emergency rescue work.
How has industry 1.0 to 4.0 influenced particulate emissions and monitoring p...Pompilia Sopco
ENVEA have been at the forefront of environmental monitoring and process control over four decades and with the emergence of the industrial internet of things (Industry 4.0) ENVEA are yet again providing innovative solutions which harness the potential of this new industrial era. At Clean Air Technology Expo taking place on 11-12 September at the NEC, Birmingham, ENVEA has demonstrate its range of Particulate Emissions Instruments alongside its advancements in data capture, storage and analytics that will combine the world of industrial particulate and flow monitoring with the latest in smart technology. In this series of articles, we will be exploring the relationship between industrialisation and particulates alongside the emergence of particulate abatement, monitoring and regulation through each of the four industrial eras.
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...CRL Asia
Presentation file on Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysimeter experiment of Thailand (Created: SWGA Chart Chiemchaisri)
1. Consider a 400-MW, 32 percent efficient coal-fired power plan.docxjeremylockett77
1. Consider a 400-MW, 32 percent efficient coal-fired power plant that uses cooling water withdrawn from a nearby river (with an upstream flow of 10-m3/s and temperature 20 °C) to take care of waste heat. The heat content of the coal is 8,000 Btu/lb, the carbon content is 60% by mass, and the sulfur content is 2% by mass.
i. How much electricity (in kWh/yr) would the plant produce each year?
ii. How many pounds per hour of coal would need to be burned at the plant?
iii. Estimate the annual carbon emissions from the plant (in metric tons C/year).
iv. Convert the carbon emissions to g C/kJ of energy produced. Compare your answer to that in Problem 2.7 of Homework 3 for petroleum combustion, and Example 2-3 for methane combustion. Comment on why coal is considered the “dirtiest” fossil fuel!
v. If the cooling water is only allowed to rise in temperature by 10 °C, what flow rate (in m3/s) from the stream would be required? Is this sustainable? What would you recommend?
vi. What would be the river temperature if all the waste heat was transferred to the river water assuming no heat losses during transfer? Would that be a problem? Why or why not.
vii. Estimate the hourly SO2 emissions (in kg/h) from the plant assuming that all the sulfur is oxidized to SO2 during combustion.
viii. What would be the problem in releasing SO2 to the atmosphere? Is sulfur dioxide a regulated priority pollutant? If yes, report the NAAQS?
ix. How would you propose to remove sulfur dioxide at the power plant?
x. Report on the required efficiency (in removal %) of the SO2 scrubber, if the plant is only allowed to emit the legal limit of 0.6 lb SO2 per million Btu of heat input.
xi. How much particulate matter could be released (in kg/year particulates) if the plant met New Source Performance Standards (NSPS) that limit particulate emissions to 0.03 lb per 106 Btu heat?
xii. Comment on the sources of particulates in the plant emissions? We have seen a dramatic decrease in particulate emissions since the 1970 Clean Air Act. How are particulate emissions controlled at stationary sources?
2. Consider an area-source box model for air pollution above a peninsula of land. The length of the box is 50 km, its width is 20 km, and a radiation inversion restricts mixing to 20 m. Wind is blowing clean air into the long dimension of the box at 0.4 m/s. Between 8 and 10 a.m. there are 300,000 vehicles on the road, each being driven 50 km, and each emitting 4 g CO/km. CO gets oxidized to carbon dioxide in the atmosphere. The half-life for CO in the atmosphere is 3 hours. Assume air temperature is 20⁰C.
i. Estimate the steady state CO concentration in the air shed (in mg/m3)
ii. Convert to ppmv and determine whether it exceeds the NAAQS.
iii. If there was no CO at 8 a.m., determine the CO concentration(in mg/m3) at 10 o’clock.
iv. How would air quality change if the wind speed picked up to 20 mph (miles per hour)? Here you need to recalculate the steady state CO concentration (in mg/m3). ...
1. Consider a 400-MW, 32 percent efficient coal-fired power plan.docxstilliegeorgiana
1. Consider a 400-MW, 32 percent efficient coal-fired power plant that uses cooling water withdrawn from a nearby river (with an upstream flow of 10-m3/s and temperature 20 °C) to take care of waste heat. The heat content of the coal is 8,000 Btu/lb, the carbon content is 60% by mass, and the sulfur content is 2% by mass.
i. How much electricity (in kWh/yr) would the plant produce each year?
ii. How many pounds per hour of coal would need to be burned at the plant?
iii. Estimate the annual carbon emissions from the plant (in metric tons C/year).
iv. Convert the carbon emissions to g C/kJ of energy produced. Compare your answer to that in Problem 2.7 of Homework 3 for petroleum combustion, and Example 2-3 for methane combustion. Comment on why coal is considered the “dirtiest” fossil fuel!
v. If the cooling water is only allowed to rise in temperature by 10 °C, what flow rate (in m3/s) from the stream would be required? Is this sustainable? What would you recommend?
vi. What would be the river temperature if all the waste heat was transferred to the river water assuming no heat losses during transfer? Would that be a problem? Why or why not.
vii. Estimate the hourly SO2 emissions (in kg/h) from the plant assuming that all the sulfur is oxidized to SO2 during combustion.
viii. What would be the problem in releasing SO2 to the atmosphere? Is sulfur dioxide a regulated priority pollutant? If yes, report the NAAQS?
ix. How would you propose to remove sulfur dioxide at the power plant?
x. Report on the required efficiency (in removal %) of the SO2 scrubber, if the plant is only allowed to emit the legal limit of 0.6 lb SO2 per million Btu of heat input.
xi. How much particulate matter could be released (in kg/year particulates) if the plant met New Source Performance Standards (NSPS) that limit particulate emissions to 0.03 lb per 106 Btu heat?
xii. Comment on the sources of particulates in the plant emissions? We have seen a dramatic decrease in particulate emissions since the 1970 Clean Air Act. How are particulate emissions controlled at stationary sources?
2. Consider an area-source box model for air pollution above a peninsula of land. The length of the box is 50 km, its width is 20 km, and a radiation inversion restricts mixing to 20 m. Wind is blowing clean air into the long dimension of the box at 0.4 m/s. Between 8 and 10 a.m. there are 300,000 vehicles on the road, each being driven 50 km, and each emitting 4 g CO/km. CO gets oxidized to carbon dioxide in the atmosphere. The half-life for CO in the atmosphere is 3 hours. Assume air temperature is 20⁰C.
i. Estimate the steady state CO concentration in the air shed (in mg/m3)
ii. Convert to ppmv and determine whether it exceeds the NAAQS.
iii. If there was no CO at 8 a.m., determine the CO concentration(in mg/m3) at 10 o’clock.
iv. How would air quality change if the wind speed picked up to 20 mph (miles per hour)? Here you need to recalculate the steady state CO concentration (in mg/m3)..
Samples of Competitive Examination Questions: Part XXXXXIAli I. Al-Mosawi
كتاب (نماذج أسئلة الإمتحان التنافسي/ إعداد علي إبراهيم الموسوي)
الجزء الواحد والخمسون:
دكتوراه جغرافية كلية التربية جامعة واسط ... ماجستير جغرافية كلية التربية جامعة واسط ... ماجستير تقنيات إدارة الجودة الشاملة الكلية التقنية الإدارية/ بغداد ... ماجستير تقنيات العمليات الكلية التقنية الإدارية/ بغداد ... إختبار اللغة الإنكليزية الكلية التقنية الإدارية/ بغداد ... ماجستير التقنيات المالية والمحاسبية الكلية التقنية الإدارية/ بغداد ... ماجستير معلوماتية قسم المعلوماتية الكلية التقنية الإدارية/ بغداد ... ماجستير هندسة كيمياوية كلية الهندسة جامعة تكريت.
Prediction of atmospheric pollution using neural networks model of fine parti...IJECEIAES
This work shows an application based on neural networks to determine the prediction of air pollution, especially particulate material of 2.5 micrometers length. This application is considered of great importance due to the impact on human health and high impact due to the agglomeration of people in cities. The implementation is performed using data captured from several devices that can be installed in specific locations for a particular geographical environment, especially in the locality of Kennedy in Bogotá. The model obtained can be used for the design of public policies that control air quality.
Accuracy Improvement of PM Measuring Instrumentsijtsrd
The PM10 concentration in the underground areas should be monitored to protect the health of the commuters in the underground subway system. The purpose of this work is to study the reliability of the instruments using light scattering method to measure the PM10 concentrations continuously. A linear regression analysis method is used to improve the performance of the instruments using light scattering method. Some experimental results show that a linear regression technique would be very helpful for the performance improvement of light scattering instruments such as Air test PM2500 and HCT 4103. Tae-In Hyon | Gyu-Sik Kim "Accuracy Improvement of PM Measuring Instruments" Published in International Journal of Trend in Scientific Research and Development (ijtsrd), ISSN: 2456-6470, Volume-3 | Issue-5 , August 2019, URL: https://www.ijtsrd.com/papers/ijtsrd26722.pdfPaper URL: https://www.ijtsrd.com/engineering/electrical-engineering/26722/accuracy-improvement-of-pm-measuring-instruments/tae-in-hyon
Online Detection of Shutdown Periods in Chemical Plants: A Case StudyManuel Martín
In process industry, chemical processes are controlled and monitored by using readings from multiple physical sensors across the plants. Such physical sensors are also supplemented by soft sensors, i.e. adaptive predictive models, which are often used for computing hard-to-measure variables of the process. For soft sensors to work well and adapt to changing operating conditions they need to be provided with relevant data. As production plants are regularly stopped, data instances generated during shutdown periods have to be identified to avoid updating these predictive models with wrong data. We present a case study concerned with a large chemical plant operation over a 2 years period. The task is to robustly and accurately identify the shutdown periods even in case of multiple sensor failures. State-of-the-art methods were evaluated using the first half of the dataset for calibration purposes and the other half for measuring the performance. Results show that shutdowns (i.e. sudden changes) can be quickly detected in any case but the detection delay of startups (i.e. gradual changes) is directly related with the choice of a window size.
Performance Analysis of Multi-Body Modeled Washing Machines (MBomWM)Dr. Amarjeet Singh
One of the key features of an automated washing machine is the noise and vibration it produces, or more technically, the decibel level it produces. Numerous of home appliance companies have put in much effort to solve this problem but there is still large room for further improvements especially in the rinse and the spin cycles of a washing machine. This work illustrates the performances of multi-body modelled of washing machines realized with the aim to analyze the vibrational acoustic emission. An experimental measurement has been carried out using a digital sound level meter (SLM) to determine the overall noise produced by four different modelled of automated washing machines with a view of noting the model with the highest sound pressure level during the three different cycles (the wash, rinse and spin). Results show that all the machines produced their highest noise during the spinning cycle. Out of the four different models considered, IPSO HF: 304 has the highest sound level of 99.62dB during its spin cycle when a maximum load of 30Kg was applied, followed by Imesa RC 23 with a 96.13dB. On the other hands, LG: Direct Drive 13 has the least sound pressure level of 84.75 dB. With this knowledge in mind, one can advise a buyer of which model to purchase from the market and if an operator must use the machine, how long he can operate such machine without health challenges.
Prediction of pollutants emissions dispersion of phosphate fertilizers produc...eSAT Journals
Abstract This study aims to the prediction of pollutants emissions dispersion of a 1 M·ton/year phosphate fertilizer facility, which is located at El-Menya Governorate, Egypt. ALOHA air dispersion software is used to predict the pollutant emissions dispersion from different stacks in the proposed project. The estimated total pollutant emissions from the proposed project are 3180 g/m3 of hydrogen fluoride (HF), 72000 g/m3 of sulfur dioxide (SO2), 14700 g/m3 of sulfur tri-oxide (SO3), 2700 g/m3 of ammonia (NH3), and 53550 g/m3 of particulates (PM). Based on the total pollutant emissions from the project, the concentrations of the investigated pollution emissions at 0.5 km, 1 km and 2 km downstream the source at the worst case scenario are obtained and compared with the allowed limits. It has been found that all the emissions resulted from different activities in the proposed project are much lower than the allowed limits specified by the Egyptian ministry of environment in Law 4/1994, and therefore the proposed project is not expected to cause any undesirable impacts on the surrounding environment. Index Terms: Air pollution; Air dispersion modeling; Environmental impact assessment; Phosphate fertilizer industry.
Turkey vs Georgia Tickets: Turkey's Road to Glory and Building Momentum for U...Eticketing.co
Euro Cup Germany fans worldwide can book Euro 2024 Tickets from our online platform www.eticketing.co.Fans can book Euro Cup 2024 Tickets on our website at discounted prices.
Euro Cup international supporters can book Euro 2024 Tickets from our online platform Worldwideticketsandhospitality.com. Followers can book Turkey Vs Portugal Tickets on our website at sale prices.
Development of Ammonia Gas Leak Detection and Location MethodTELKOMNIKA JOURNAL
This paper proposed the gas for industrial ammonia leak diffusion model and the Gauss method
of leakage localization. A set of wireless ammonia leak alarm system is composed of sensor node, network
coordinator and host used in the industrial field was developed, the purpose is to reduce the loss of
property caused by the leakage of ammonia industry. Using the monitoring system to carry out the
ammonia leak location simulation measurement experiment, the result shows that the relative positioning
error of the monitoring system is about 12%, which meets the needs of industrial production safety
monitoring. Using the wireless sensor network to monitor the concentration of ammonia gas and locate the
leakage source, it solves the problems of traditional wired alarm system, such as difficult wiring and weak
expansibility, which helps to find the leak timely and provides a reference for the emergency rescue work.
How has industry 1.0 to 4.0 influenced particulate emissions and monitoring p...Pompilia Sopco
ENVEA have been at the forefront of environmental monitoring and process control over four decades and with the emergence of the industrial internet of things (Industry 4.0) ENVEA are yet again providing innovative solutions which harness the potential of this new industrial era. At Clean Air Technology Expo taking place on 11-12 September at the NEC, Birmingham, ENVEA has demonstrate its range of Particulate Emissions Instruments alongside its advancements in data capture, storage and analytics that will combine the world of industrial particulate and flow monitoring with the latest in smart technology. In this series of articles, we will be exploring the relationship between industrialisation and particulates alongside the emergence of particulate abatement, monitoring and regulation through each of the four industrial eras.
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...CRL Asia
Presentation file on Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysimeter experiment of Thailand (Created: SWGA Chart Chiemchaisri)
1. Consider a 400-MW, 32 percent efficient coal-fired power plan.docxjeremylockett77
1. Consider a 400-MW, 32 percent efficient coal-fired power plant that uses cooling water withdrawn from a nearby river (with an upstream flow of 10-m3/s and temperature 20 °C) to take care of waste heat. The heat content of the coal is 8,000 Btu/lb, the carbon content is 60% by mass, and the sulfur content is 2% by mass.
i. How much electricity (in kWh/yr) would the plant produce each year?
ii. How many pounds per hour of coal would need to be burned at the plant?
iii. Estimate the annual carbon emissions from the plant (in metric tons C/year).
iv. Convert the carbon emissions to g C/kJ of energy produced. Compare your answer to that in Problem 2.7 of Homework 3 for petroleum combustion, and Example 2-3 for methane combustion. Comment on why coal is considered the “dirtiest” fossil fuel!
v. If the cooling water is only allowed to rise in temperature by 10 °C, what flow rate (in m3/s) from the stream would be required? Is this sustainable? What would you recommend?
vi. What would be the river temperature if all the waste heat was transferred to the river water assuming no heat losses during transfer? Would that be a problem? Why or why not.
vii. Estimate the hourly SO2 emissions (in kg/h) from the plant assuming that all the sulfur is oxidized to SO2 during combustion.
viii. What would be the problem in releasing SO2 to the atmosphere? Is sulfur dioxide a regulated priority pollutant? If yes, report the NAAQS?
ix. How would you propose to remove sulfur dioxide at the power plant?
x. Report on the required efficiency (in removal %) of the SO2 scrubber, if the plant is only allowed to emit the legal limit of 0.6 lb SO2 per million Btu of heat input.
xi. How much particulate matter could be released (in kg/year particulates) if the plant met New Source Performance Standards (NSPS) that limit particulate emissions to 0.03 lb per 106 Btu heat?
xii. Comment on the sources of particulates in the plant emissions? We have seen a dramatic decrease in particulate emissions since the 1970 Clean Air Act. How are particulate emissions controlled at stationary sources?
2. Consider an area-source box model for air pollution above a peninsula of land. The length of the box is 50 km, its width is 20 km, and a radiation inversion restricts mixing to 20 m. Wind is blowing clean air into the long dimension of the box at 0.4 m/s. Between 8 and 10 a.m. there are 300,000 vehicles on the road, each being driven 50 km, and each emitting 4 g CO/km. CO gets oxidized to carbon dioxide in the atmosphere. The half-life for CO in the atmosphere is 3 hours. Assume air temperature is 20⁰C.
i. Estimate the steady state CO concentration in the air shed (in mg/m3)
ii. Convert to ppmv and determine whether it exceeds the NAAQS.
iii. If there was no CO at 8 a.m., determine the CO concentration(in mg/m3) at 10 o’clock.
iv. How would air quality change if the wind speed picked up to 20 mph (miles per hour)? Here you need to recalculate the steady state CO concentration (in mg/m3). ...
1. Consider a 400-MW, 32 percent efficient coal-fired power plan.docxstilliegeorgiana
1. Consider a 400-MW, 32 percent efficient coal-fired power plant that uses cooling water withdrawn from a nearby river (with an upstream flow of 10-m3/s and temperature 20 °C) to take care of waste heat. The heat content of the coal is 8,000 Btu/lb, the carbon content is 60% by mass, and the sulfur content is 2% by mass.
i. How much electricity (in kWh/yr) would the plant produce each year?
ii. How many pounds per hour of coal would need to be burned at the plant?
iii. Estimate the annual carbon emissions from the plant (in metric tons C/year).
iv. Convert the carbon emissions to g C/kJ of energy produced. Compare your answer to that in Problem 2.7 of Homework 3 for petroleum combustion, and Example 2-3 for methane combustion. Comment on why coal is considered the “dirtiest” fossil fuel!
v. If the cooling water is only allowed to rise in temperature by 10 °C, what flow rate (in m3/s) from the stream would be required? Is this sustainable? What would you recommend?
vi. What would be the river temperature if all the waste heat was transferred to the river water assuming no heat losses during transfer? Would that be a problem? Why or why not.
vii. Estimate the hourly SO2 emissions (in kg/h) from the plant assuming that all the sulfur is oxidized to SO2 during combustion.
viii. What would be the problem in releasing SO2 to the atmosphere? Is sulfur dioxide a regulated priority pollutant? If yes, report the NAAQS?
ix. How would you propose to remove sulfur dioxide at the power plant?
x. Report on the required efficiency (in removal %) of the SO2 scrubber, if the plant is only allowed to emit the legal limit of 0.6 lb SO2 per million Btu of heat input.
xi. How much particulate matter could be released (in kg/year particulates) if the plant met New Source Performance Standards (NSPS) that limit particulate emissions to 0.03 lb per 106 Btu heat?
xii. Comment on the sources of particulates in the plant emissions? We have seen a dramatic decrease in particulate emissions since the 1970 Clean Air Act. How are particulate emissions controlled at stationary sources?
2. Consider an area-source box model for air pollution above a peninsula of land. The length of the box is 50 km, its width is 20 km, and a radiation inversion restricts mixing to 20 m. Wind is blowing clean air into the long dimension of the box at 0.4 m/s. Between 8 and 10 a.m. there are 300,000 vehicles on the road, each being driven 50 km, and each emitting 4 g CO/km. CO gets oxidized to carbon dioxide in the atmosphere. The half-life for CO in the atmosphere is 3 hours. Assume air temperature is 20⁰C.
i. Estimate the steady state CO concentration in the air shed (in mg/m3)
ii. Convert to ppmv and determine whether it exceeds the NAAQS.
iii. If there was no CO at 8 a.m., determine the CO concentration(in mg/m3) at 10 o’clock.
iv. How would air quality change if the wind speed picked up to 20 mph (miles per hour)? Here you need to recalculate the steady state CO concentration (in mg/m3)..
Samples of Competitive Examination Questions: Part XXXXXIAli I. Al-Mosawi
كتاب (نماذج أسئلة الإمتحان التنافسي/ إعداد علي إبراهيم الموسوي)
الجزء الواحد والخمسون:
دكتوراه جغرافية كلية التربية جامعة واسط ... ماجستير جغرافية كلية التربية جامعة واسط ... ماجستير تقنيات إدارة الجودة الشاملة الكلية التقنية الإدارية/ بغداد ... ماجستير تقنيات العمليات الكلية التقنية الإدارية/ بغداد ... إختبار اللغة الإنكليزية الكلية التقنية الإدارية/ بغداد ... ماجستير التقنيات المالية والمحاسبية الكلية التقنية الإدارية/ بغداد ... ماجستير معلوماتية قسم المعلوماتية الكلية التقنية الإدارية/ بغداد ... ماجستير هندسة كيمياوية كلية الهندسة جامعة تكريت.
Prediction of atmospheric pollution using neural networks model of fine parti...IJECEIAES
This work shows an application based on neural networks to determine the prediction of air pollution, especially particulate material of 2.5 micrometers length. This application is considered of great importance due to the impact on human health and high impact due to the agglomeration of people in cities. The implementation is performed using data captured from several devices that can be installed in specific locations for a particular geographical environment, especially in the locality of Kennedy in Bogotá. The model obtained can be used for the design of public policies that control air quality.
Accuracy Improvement of PM Measuring Instrumentsijtsrd
The PM10 concentration in the underground areas should be monitored to protect the health of the commuters in the underground subway system. The purpose of this work is to study the reliability of the instruments using light scattering method to measure the PM10 concentrations continuously. A linear regression analysis method is used to improve the performance of the instruments using light scattering method. Some experimental results show that a linear regression technique would be very helpful for the performance improvement of light scattering instruments such as Air test PM2500 and HCT 4103. Tae-In Hyon | Gyu-Sik Kim "Accuracy Improvement of PM Measuring Instruments" Published in International Journal of Trend in Scientific Research and Development (ijtsrd), ISSN: 2456-6470, Volume-3 | Issue-5 , August 2019, URL: https://www.ijtsrd.com/papers/ijtsrd26722.pdfPaper URL: https://www.ijtsrd.com/engineering/electrical-engineering/26722/accuracy-improvement-of-pm-measuring-instruments/tae-in-hyon
Online Detection of Shutdown Periods in Chemical Plants: A Case StudyManuel Martín
In process industry, chemical processes are controlled and monitored by using readings from multiple physical sensors across the plants. Such physical sensors are also supplemented by soft sensors, i.e. adaptive predictive models, which are often used for computing hard-to-measure variables of the process. For soft sensors to work well and adapt to changing operating conditions they need to be provided with relevant data. As production plants are regularly stopped, data instances generated during shutdown periods have to be identified to avoid updating these predictive models with wrong data. We present a case study concerned with a large chemical plant operation over a 2 years period. The task is to robustly and accurately identify the shutdown periods even in case of multiple sensor failures. State-of-the-art methods were evaluated using the first half of the dataset for calibration purposes and the other half for measuring the performance. Results show that shutdowns (i.e. sudden changes) can be quickly detected in any case but the detection delay of startups (i.e. gradual changes) is directly related with the choice of a window size.
Performance Analysis of Multi-Body Modeled Washing Machines (MBomWM)Dr. Amarjeet Singh
One of the key features of an automated washing machine is the noise and vibration it produces, or more technically, the decibel level it produces. Numerous of home appliance companies have put in much effort to solve this problem but there is still large room for further improvements especially in the rinse and the spin cycles of a washing machine. This work illustrates the performances of multi-body modelled of washing machines realized with the aim to analyze the vibrational acoustic emission. An experimental measurement has been carried out using a digital sound level meter (SLM) to determine the overall noise produced by four different modelled of automated washing machines with a view of noting the model with the highest sound pressure level during the three different cycles (the wash, rinse and spin). Results show that all the machines produced their highest noise during the spinning cycle. Out of the four different models considered, IPSO HF: 304 has the highest sound level of 99.62dB during its spin cycle when a maximum load of 30Kg was applied, followed by Imesa RC 23 with a 96.13dB. On the other hands, LG: Direct Drive 13 has the least sound pressure level of 84.75 dB. With this knowledge in mind, one can advise a buyer of which model to purchase from the market and if an operator must use the machine, how long he can operate such machine without health challenges.
Prediction of pollutants emissions dispersion of phosphate fertilizers produc...eSAT Journals
Abstract This study aims to the prediction of pollutants emissions dispersion of a 1 M·ton/year phosphate fertilizer facility, which is located at El-Menya Governorate, Egypt. ALOHA air dispersion software is used to predict the pollutant emissions dispersion from different stacks in the proposed project. The estimated total pollutant emissions from the proposed project are 3180 g/m3 of hydrogen fluoride (HF), 72000 g/m3 of sulfur dioxide (SO2), 14700 g/m3 of sulfur tri-oxide (SO3), 2700 g/m3 of ammonia (NH3), and 53550 g/m3 of particulates (PM). Based on the total pollutant emissions from the project, the concentrations of the investigated pollution emissions at 0.5 km, 1 km and 2 km downstream the source at the worst case scenario are obtained and compared with the allowed limits. It has been found that all the emissions resulted from different activities in the proposed project are much lower than the allowed limits specified by the Egyptian ministry of environment in Law 4/1994, and therefore the proposed project is not expected to cause any undesirable impacts on the surrounding environment. Index Terms: Air pollution; Air dispersion modeling; Environmental impact assessment; Phosphate fertilizer industry.
Turkey vs Georgia Tickets: Turkey's Road to Glory and Building Momentum for U...Eticketing.co
Euro Cup Germany fans worldwide can book Euro 2024 Tickets from our online platform www.eticketing.co.Fans can book Euro Cup 2024 Tickets on our website at discounted prices.
Euro Cup international supporters can book Euro 2024 Tickets from our online platform Worldwideticketsandhospitality.com. Followers can book Turkey Vs Portugal Tickets on our website at sale prices.
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Mats André Zuccarello Aasen, commonly known as Mats Zuccarello, was born on September 1, 1987, in
Oslo, Norway. He grew up in the bustling neighborhood of Løren, where his passion for ice hockey began
at a young age. His mother, Anita Zuccarello, is of Italian descent, and his father, Glenn Aasen, is
Norwegian. This multicultural background played a significant role in shaping his identity and versatility
on and off the ice.
Spain vs Italy Spain at Euro Cup 2024 Group, Fixtures, Players to Watch and M...Eticketing.co
Euro Cup 2024 fans worldwide can book Spain vs Italy Tickets from our online platform www.eticketing.co. Fans can book Euro Cup Germany Tickets on our website at discounted prices.
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Denmark vs England England Euro Cup squad guide Fixtures, predictions and bes...Eticketing.co
We offer UEFA Euro 2024 Tickets to admirers who can get Denmark vs England Tickets through our trusted online ticketing marketplace. Eticketing. co is the most reliable source for booking Euro Cup Final Tickets. Sign up for the latest Euro Cup Germany Ticket alert.
Ukraine Euro Cup 2024 Squad Sergiy Rebrov's Selections and Prospects.docxEuro Cup 2024 Tickets
After securing their spot through the playoff route, Ukraine is gearing up for their fourth consecutive European Championship. Ukraine first qualified as hosts in 2012, but in 2016
Euro Cup fans worldwide can book Euro 2024 Tickets from our online platform www.worldwideticketsandhospitality. Fans can book Slovenia Vs Denmark Tickets on our website at discounted prices.
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Mock 2024 NHL Draft Experts Divided after Celebrini, Levshunov, Silayev go in...Ice Brek
After the NHL Draft Lottery on Monday, Adam Kimelman, NHL.com’s deputy managing editor,
and Mike G., senior draft writer, Morreale make their predictions for how the first 16 selections
of the 2024 Upper Deck NHL Draft could turn out.
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Results for LtCol Thomas Jasper, Marine, for the 2010 Marine Corps Marathon held October 31, 2010, marking the 35th annual marathon known as "The People's Marathon."
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Air modelling presentation final2
1. Asian Institute of Technology
Air Pollutant Modelling and Its Application
“Evaluation of CO Concentration Level
in Delhi by Muair2.0, ISC3 & Caline4”
Prepared by:
Miss. Thiri Tin Htut
Mr. Bishal Bhari
Mr. Visal Yoeung
Mr. Pongsakorn Chaichai
May 1, 2014
3. Introduction
A.P.Mod. Plays a vital role in A.P Control and
management
A.P modelling software are built with different
assumption and computation methods
Accuracy of the model depends on different
factors
3
4. Objectives
To get acquainted with A.P.Mod1
To model the CO concentration in
Delhi for the year 20022
To compare and analyze the result
from different model3
4
8. About MUAIR2.0
Developed for the transport project within the ARRPEEC
(AITT)
Predicts impact of emission from Urban area
MUAIR is a 2D, multi-box dispersion model
Uses mathematical formula of Atmospheric Turbulence
and Diffusion Laboratory (ATDL) Model
Height of the top lid proportional to the vertical dispersion
parameter
Integral form of the Gaussian plume model and treats an
area source as an infinite array of infinitesimal point
sources
8
9. Basic Features of MUAIR2.0
Applicable for less reactive pollutant like CO
Does not consider chemical transformation
First 5 stability classes
Uses wind direction in degrees (0-360) and wind
speed in m/s
Can’t handle calm wind
Output in mg/m3 or μg/m3
9
10. Case A: For all Area sources
2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
1st highest hourly concentration (m iligram /m 3)
0
20
40
60
80
100
120
140
160
180
200
220
240
260
280
2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
A v e ra g e h o u rly c o n c e n tra tio n (m ilig ra m /m 3 )
0
5
1 0
1 5
2 0
2 5
3 0
3 5
4 0
4 5
5 0
5 5
6 0
6 5
7 0
7 5
8 0
20 HH Conc
Highest concentration for an
hour occurred in 20th April
2002 at the (12500,6500)
domain with the
concentration of 271.39
mg/m3 CO concentration.
20 HAAvg Conc
Highest average annual
concentration of 78.83
mg/m3 occurred at (12500,
6500)
10
11. Case B: For 5 selected/marked
red grid area sources
20 HH Conc
Highest concentration for an
hour occurred in 12th April
2002 at the (12500,12500)
domain with the
concentration of 134.82
mg/m3 CO concentration.
20 HAAvg Conc
Highest average annual
concentration of 36.56
mg/m3 occurred at (12500,
12500)
2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
32
34
36
38
A ve ra g e h o u rly co n ce n tra tio n (m ilig ra m /m 3 )2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
0
5
1 0
1 5
2 0
2 5
3 0
3 5
4 0
4 5
5 0
5 5
6 0
6 5
7 0
7 5
8 0
8 5
9 0
9 5
1 0 0
1 0 5
1 1 0
1 1 5
1 2 0
1 2 5
1 3 0
1 3 5
1st highest hourly concentration (m iligram /m 3)
11
12. Case C: For Point sources emission
20 HH Conc
Highest concentration for an
hour occurred in 11th April
2002 at the (14500,9500)
domain with the
concentration of 34.93
mg/m3 CO concentration.
20 HAAvg Conc
Highest average annual
concentration of 10.61
mg/m3 occurred at (14500,
9500)
2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
0
0 .5
1
1 .5
2
2 .5
3
3 .5
4
4 .5
5
5 .5
6
6 .5
7
7 .5
8
8 .5
9
9 .5
1 0
1 0 .5
1 1
A v e ra g e h o u rly c o n c e n tra tio n (m ilig ra m /m 3 )2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
0
2
4
6
8
1 0
1 2
1 4
1 6
1 8
2 0
2 2
2 4
2 6
2 8
3 0
3 2
3 4
3 6
1 s t h ig h e s t h o u rly c o n c e n tra tio n (m ilig ra m /m 3 )
12
13. Case D: For all 5 marked area sources
and point sources
20 HH Conc
Highest concentration for an
hour occurred in 12th April
2002 at the (12500,8500)
domain with the
concentration of 144.09
mg/m3 CO concentration.
20 HAAvg Conc
Highest average annual
concentration of 38.55
mg/m3 occurred at (11500,
9500)
2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
0
2
4
6
8
1 0
1 2
1 4
1 6
1 8
2 0
2 2
2 4
2 6
2 8
3 0
3 2
3 4
3 6
3 8
4 0
A v e ra g e h o u rly c o n c e n tra tio n (m ilig ra m /m 3 )
2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0
2 0 0 0
4 0 0 0
6 0 0 0
8 0 0 0
1 0 0 0 0
1 2 0 0 0
1 4 0 0 0
1 6 0 0 0
0
10
20
30
40
50
60
70
80
90
100
110
120
130
140
150
1 s t h ig h e s t h o u rly c o n c e n tra tio n (m ilig ra m /m 3 )
13
14. Summary of all case
A B C D
Hourly 271.39 134.82 34.93 144.09
Annual 78.83 36.56 10.61 38.55
(12500,6500)
(12500,12500)
(14500,9500)
(12500,8500)
(12500,6500)
(12500,12500)
(12500,8500)
(11500,9500)
0
50
100
150
200
250
300
350
400
450
Concentration(mg/cu.m)
Case A: Area Souce
Case B: Selected Grid Area Source
Case C: Point Source
Case D: Marked Area Source & Point Source
14
15. Monthly Avg. CO Conc. at
the Receptor
• R3 had the highest concentration throughout the year
• R4 was not affected by the point and area sources since it is located far
from the combined source
• R3 and Receptor R5 received the highest concentration of CO for the
month from October to March
15
17. About ISC
ISC (Industrial Source Complex) model is a steady-state
Gaussian plume model which can be used to assess pollutant
concentrations from a wide variety of sources associated with
an industrial complex.
This model can account for the following:
Point, area, line, and volume sources
Settling and dry deposition of particles
Downwash
Separation of point sources
Limited terrain adjustment
17
18. Input data Requirements
Source data
Dimensions of the source
Emission discharge rate
Release height of the emission source
18
Meteorological data
Ambient temperature, K
Wind flow
Wind speed, m/s
Atmospheric stability classes (A
through F)
Urban and rural mixing height, m
19. 20 HH Conc.
Highest concentration for an
hour occurred in 11th Feb 2002
at the (12000,9000) domain
with the concentration of
37.09 mg/m3 CO
concentration.
20 HAAvg Conc.
Highest average annual
concentration of 11.28
mg/m3 occurred at (12000,
9000)
Case B: For 5 selected/marked
red grid area sources
1st highest for hourly CO concentration
Annual average CO concentration
19
20. 20 HH Conc.
Highest concentration for an
hour occurred in 1sh Oct 2002
at the (15000,15000) domain
with the concentration of 0.25
mg/m3 CO concentration.
20 HAAvg Conc.
Highest average annual
concentration of 0.0086
mg/m3 occurred at (11000,
11000)
1st highest for hourly CO concentration
Annual average CO concentration
Case C: For Point sources emission 20
21. 20 HH Conc.
Highest concentration for an
hour occurred in 20th May 2002
at the (12000,9000) domain with
the concentration of 37.11
mg/m3 CO concentration.
20 HAAvg Conc.
Highest average annual
concentration of 11.29
mg/m3 occurred at (12000,
9000)
1st highest for hourly CO concentration
Annual average CO concentration
Case D: For all 5 marked area sources
and point sources 21
22. The contribution of each
source type
4.72%
2.97%
92.31%
R3 R4 R5
Receptor
Concentratio
n (mg/m3)
R3 0.39
R4 0.25
R5 7.6
Total 8.26
Contribution of each source type to the annual
average CO at receptor R3,R4 and R5
22
23. Compare the results of
MUAIR and ISC models
Case
MUAIR
1st highest
hourly
(mg/m3)
Coordinate
(X,Y)
1st annual
average
(mg/m3)
Coordinate
(X,Y)
B 134.82 12500,12500 36.56 12500,12500
C 34.93 14500,9500 10.61 14500,9500
D 144.09 12500,8500 38.55 11500,9500
ISC
B 37.09 12000,9000 11.28 12000,9000
C 0.25 15000,15000 0.009 11000,11000
D 37.11 12000,9000 11.29 12000,9000
B C D B C D
1st highest hourly 1st annual average
MUAIR
ISC
** The ISC grids are shifted by a half of grid (500
m) in both X and Y directions in order to
compared with MUAIR results.
23
25. Concentration of Area Sources
20 HH Conc.
Highest concentration for
an hour occurred in 20th
May 2002 at the
(12000,9000) domain with
the concentration of 37.09
mg/m3 CO concentration.
1st H annual Conc.
1st Highest concentration for
an annual occurred at the
(12000,9000) domain with
the concentration of 7.52
mg/m3 CO concentration.
Concentration of Point Sources
20 HH Conc.
Highest concentration for
an hour occurred in 1st Oct
2002 at the (15000,15000)
domain with the
concentration of 0.25
mg/m3 CO concentration.
1st H annual Conc.
1st Highest concentration for
an annual occurred at the
(11000,11000) domain with
the concentration of 0.0087
mg/m3 CO concentration.
25
26. Concentration of Combined Sources
20 HH Conc.
Highest concentration for
an hour occurred in 20th
May 2002 at the
(12000,9000) domain with
the concentration of 37.11
mg/m3 CO concentration.
1st H annual Conc.
1st Highest concentration for
an annual occurred at the
(12000,9000) domain with
the concentration of 7.53
mg/m3 CO concentration.
Comparison the first HH and HA Conc of ISC
Part 1 and Part 2
Case
ISC PART 1
1st highest
hourly
(mg/m3)
Coordinate
(X,Y)
1st highest
annual
(mg/m3)
Coordinate
(X,Y)
Area 37.09 12000,9000 11.28 12000,9000
Point 0.25 15000,15000 0.01 11000,11000
Combined 37.11 12000,9000 11.29 12000,9000
ISC PART 2
Area 37.09 12000,9000 7.52 12000,9000
Point 0.25 15000,15000 0.01 11000,11000
Combined 37.11 12000,9000 7.53 12000,9000
In Part 2, the emission
from the area sources
were reduced by 50%
during daytime (6:00am
to 6:00pm) which
effected in the ISC
model running result that
the Part 2 is lower
concentration than Part
1 in area source and
combined source in
26
27. Comparison annual Avg CO Conc at
receptor R3, R4 and R5
Case Concentration ((µg/m3)
R3 R4 R5
Area 242.27338 150.96539 5051.03174
Point 4.53533 5.25978 4.99416
Combined 246.80685 156.22371 5055.95752
0
1000
2000
3000
4000
5000
6000
Area Point Combined
µg/m3
Receptor 3 Receptor 4 Receptor 5
27
29. About Caline4
Caline4 model is the 4 generation simple line source Gaussian plume
dispersion model.
Predicts the conc. CO, NO2, and PM10/ PM2.5 near roadways
(highway, arterial streets) for relatively uncomplicated terrains.
Handle up to 20 link and 20 receptors but the model cannot predict
concentration within 3 meters from lane edge
The important input parameters required
Classified traffic volume (number of vehicles per hour),
Meteorological parameters (wind speed, wind direction,
ambient temperature, mixing height and stability class)
Emission parameters (weighted emission factor, WEF), road
geometry (road width, median width, road elevation),
Type of terrain (rural or urban), background CO
concentration (ppm or µg/m3) at pre-identified receptor
locations along the road corridors.
29
30. Estimate the line source contribution to the receptor
R1- R6 with the Standard, Worst case, Multi-run, and
Multi-run-worst case
Period: 6 am of Jan 18th
2002
Wind speed: 1.2 m/s
Wind direction: the
majority of wind comes
from the East
The road is divided into
12 sections
6 receptors are placed
to measure the CO
Conc.
30
31. Estimate the line source contribution to the receptor
R1- R6 with the Standard, Worst case, Multi-run, and
Multi-run-worst case
Cases
Predicted concentration (ppm)
R1 R2 R3 R4 R5 R6
Standard 0.7 0.0 0.4 0.0 0.4 0.0
Worst Case 1.1 0.9 0.5 0.5 0.4 0.7
Standard run: highest
CO is 0.7 ppm at R1
Worst Case run: max
CO is 1.1 ppm at R1
Multi run: highest avg
co in 8 hr is 0.27 ppm
Multi run worst: Max
avg Co in 8 is 0.73
ppm
31
32. Estimate the relative contribution from each of
3 types of sources at R5
82.46
17.12
0.42
0
20
40
60
80
100
Area Line Point
Percentage(%)
32
33. Estimate the line source contribution to the
new receptors
Period: 24 hour of Jan 18
Max Wind speed: 1.2 m/s
Wind direction: the
majority of wind comes
from the South
The road is divided into 12
sections
20 receptors are placed to
predict the CO Conc.
33
34. Estimate the line source contribution to the
new receptors By Worst Case Run
Worst Case:
The hourly max of CO is 4.6
ppm at the receptor R1
Beyond 1km, there has no max
of CO > 34.2 ppm (std)
34
35. Multi run Worst Case:
The average max of every
8hrs CO conc = 2.77 ppm at
R1
1km, the max of CO conc <
10.4 ppm (std) in every8hr
Estimate the line source contribution to the
new receptors By Multi Run Worst Case 35
36. Conclusion 36
The Concentrations of CO obtained from Muair2.0 are significantly
higher than ISC for all cases. The reasons of the different
concentration results produced by the both model are:
MUAIR considers point source as area source while ISC can
handle both sources.
MUAIR uses only first 5 stability classes for calculation while stability
classes 6 and 7 are treated as class 5 in the calculation
ISC model can handle the multiple source types in the domain =>
produce the result more accurate than Muair.
For line source, Caline4 can predict the concentration at each
receptor location, resulting the different concentration levels at
each receptor. All the concentrations predicted by worst case and
Multi run worst case are higher than standard run and Multi run since
the both worse case and multi run produce the maximum
concentration at each receptor.
At receptor R1 was found highest concentration comparing to other
receptors due its location close to the road.