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CONTEXTUALIZED TO KATHMANDU VALLEY 
Prepared BY: Er. Bishnu Pd. Devkota 
067MST258
 Introduction 
 Objective of the Study 
 Literature Review 
 Research Methodology 
 Historical Background: Kathmandu Valley 
 Present Issues: Kathmandu Valley 
 Analyzing the data 
 Future Forecast: Kathmandu Valley 
 Results 
 Conclusions/Recommendations 
 References
 Urbanization: to make an area of countryside or a village 
into a town (Encarta® 2008) 
 Air Pollution: addition of harmful substances to the 
atmosphere resulting in damage to the environment, 
human health, and quality of life. (Encarta ® 2008) 
 The major source of air pollutant in many urban area is 
found as the exhaust from vehicles. 
 The previously completed research works about the air 
pollution in Kathmandu valley shows the transportation 
as the major source of pollution. 
 I have reviewed more than 10 research reports about 
Kathmandu valley and additional 10 reports from 
various parts of the world. This means that the data 
presented in this presentation are secondary data. To get 
more data I have visited a lot of government and other 
official websites that are listed in the references.
 The main objective of this study is to extract the major issues 
or sources of air pollution within the transportation 
mechanism in the context of Kathmandu valley and conclude 
for some reasonable recommendations 
 It also has the following objectives: 
 To collect various types of air pollution parameters 
 To evaluate the major sources 
 To describe the transportation as a source of air pollutant 
 To collect the major causes of air pollution within 
transportation system 
 To evaluate the causes on the basis of secondary data 
 To provide some recommendations
 Urban transport and environment in 
Kathmandu Valley by Shobhakhar Dhakal, 
Japan 
 Air pollution and role of urban transportaion in 
Kathmandu Valley by Nawaraj Khatiwada 
(SchEMS and MOPE) 
 Assessment of ambient air quality in Bishnumati 
corridor, Kathmandu metropolis 
 Kathmandu university medical journal (2003) 
vol-1, no.4, Issue 4 
 Climate and air quality : a case study by Sunil 
Pokhrel, University Edwardsville 
 CIA: Asia network, vol-5
GEOGRAPHY 
oValley area: 640 sq. km 
o Floor area: 400 sq. km 
•Kathmandu – metropolitan city 
•Kirtipur – municipality 
•Lalitpur – sub-metropolitan city 
•Bhaktapur municipality 
•Madhyapur municipality 
•VDCs
Source: July 2004, IGES
 Transportation Sector 
 City transportation and long distance travel 
 Vehicular emission 
 Resuspension of particles 
 Solid wastages dumped on the road 
 Industry 
 Brick kilns 
 Cement factory 
 Construction activities 
 3000 houses per year (1990-2000) 
 Other sources 
 Air transport 
 Tyre burning
Source: July 2004, IGES
Source: July 2004, IGES (Institute for Global Environmental Strategies)
Source: Encreta 2008
Source:
NAAQS=National Ambient Air Quality Standard 
Source: July 2004, IGES
 In 1987, EPA (Environment Protection Agency) replaced the 
earlier Total Suspended Particulate (TSP) air quality 
standard with a PM-10 standard. The new standard focuses 
on smaller particles that are likely responsible for adverse 
health effects because of their ability to reach the lower 
regions of the respiratory tract. The PM-10 standard 
includes particles with a diameter of 10 micrometers or less 
(0.0004 inches or one-seventh the width of a human hair). 
EPA's health-based national air quality standard for PM-10 
is 50 μg/m3 (measured as an annual mean) and 150 μg/m3 
(measured as a daily concentration). Major concerns for 
human health from exposure to PM-10 include: effects on 
breathing and respiratory systems, damage to lung tissue, 
cancer, and premature death. The elderly, children, and 
people with chronic lung disease, influenza, or asthma, are 
especially sensitive to the effects of particulate matter.
 In PM 10 Concentration: 
 NAAQS: 120 microgram/ cubic meter 
 Highest concentration in winter season 
 Sag in the curve coincide with rainy season 
 So2 Concentration: 
 NAAQS: 70 mocrogram/cubic meter (24 hr average) 
 Highest values in Bhaktapur 
 Operating season: December to may 
 CO Concentration: 
 NAAQS: 10,000 microgram/cubic meter (8hr 
average)
 Large scale introduction of bus system will 
reduce large no of vehicles and save energy. 
However, in absence of progressive emission 
standards this will increase PM10 and SO2 
 In long-run a number of countermeasures 
would be necessary. 
 Tightening of emission standards is necessary 
but not sufficient: effective for SO2, PM10 and 
Nox but ineffective for reducing CO2. 
 Greater use of indigenously produced energy 
resources (electricity in this case)
 Promoting public transportation, especially with 
those which high occupancy modes are essential 
for a number of factors 
 A package of countermeasures are necessary 
which only can address various priority issues 
such as PM10, congestion, energy saving, greater 
use of electricity and CO2 
 There should be synergies (coordination), not the 
conflicts, between local and global priorities in the 
Kathmandu Valley 
 Issues: Data quality (vehicle stock, operating 
factor, fuel efficiencies, emission factors)
 http://www.iges.or.jplenlue 
 www.google.com.np 
 www.kathmandu.gov.np 
 http://ces.ioe.edu.np 
 www.dor.gov.np 
 http://www.environment-agency.gov.uk/
Urban air quality and transportaion

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Urban air quality and transportaion

  • 1. CONTEXTUALIZED TO KATHMANDU VALLEY Prepared BY: Er. Bishnu Pd. Devkota 067MST258
  • 2.  Introduction  Objective of the Study  Literature Review  Research Methodology  Historical Background: Kathmandu Valley  Present Issues: Kathmandu Valley  Analyzing the data  Future Forecast: Kathmandu Valley  Results  Conclusions/Recommendations  References
  • 3.  Urbanization: to make an area of countryside or a village into a town (Encarta® 2008)  Air Pollution: addition of harmful substances to the atmosphere resulting in damage to the environment, human health, and quality of life. (Encarta ® 2008)  The major source of air pollutant in many urban area is found as the exhaust from vehicles.  The previously completed research works about the air pollution in Kathmandu valley shows the transportation as the major source of pollution.  I have reviewed more than 10 research reports about Kathmandu valley and additional 10 reports from various parts of the world. This means that the data presented in this presentation are secondary data. To get more data I have visited a lot of government and other official websites that are listed in the references.
  • 4.  The main objective of this study is to extract the major issues or sources of air pollution within the transportation mechanism in the context of Kathmandu valley and conclude for some reasonable recommendations  It also has the following objectives:  To collect various types of air pollution parameters  To evaluate the major sources  To describe the transportation as a source of air pollutant  To collect the major causes of air pollution within transportation system  To evaluate the causes on the basis of secondary data  To provide some recommendations
  • 5.  Urban transport and environment in Kathmandu Valley by Shobhakhar Dhakal, Japan  Air pollution and role of urban transportaion in Kathmandu Valley by Nawaraj Khatiwada (SchEMS and MOPE)  Assessment of ambient air quality in Bishnumati corridor, Kathmandu metropolis  Kathmandu university medical journal (2003) vol-1, no.4, Issue 4  Climate and air quality : a case study by Sunil Pokhrel, University Edwardsville  CIA: Asia network, vol-5
  • 6. GEOGRAPHY oValley area: 640 sq. km o Floor area: 400 sq. km •Kathmandu – metropolitan city •Kirtipur – municipality •Lalitpur – sub-metropolitan city •Bhaktapur municipality •Madhyapur municipality •VDCs
  • 8.  Transportation Sector  City transportation and long distance travel  Vehicular emission  Resuspension of particles  Solid wastages dumped on the road  Industry  Brick kilns  Cement factory  Construction activities  3000 houses per year (1990-2000)  Other sources  Air transport  Tyre burning
  • 10. Source: July 2004, IGES (Institute for Global Environmental Strategies)
  • 13. NAAQS=National Ambient Air Quality Standard Source: July 2004, IGES
  • 14.
  • 15.
  • 16.
  • 17.  In 1987, EPA (Environment Protection Agency) replaced the earlier Total Suspended Particulate (TSP) air quality standard with a PM-10 standard. The new standard focuses on smaller particles that are likely responsible for adverse health effects because of their ability to reach the lower regions of the respiratory tract. The PM-10 standard includes particles with a diameter of 10 micrometers or less (0.0004 inches or one-seventh the width of a human hair). EPA's health-based national air quality standard for PM-10 is 50 μg/m3 (measured as an annual mean) and 150 μg/m3 (measured as a daily concentration). Major concerns for human health from exposure to PM-10 include: effects on breathing and respiratory systems, damage to lung tissue, cancer, and premature death. The elderly, children, and people with chronic lung disease, influenza, or asthma, are especially sensitive to the effects of particulate matter.
  • 18.
  • 19.  In PM 10 Concentration:  NAAQS: 120 microgram/ cubic meter  Highest concentration in winter season  Sag in the curve coincide with rainy season  So2 Concentration:  NAAQS: 70 mocrogram/cubic meter (24 hr average)  Highest values in Bhaktapur  Operating season: December to may  CO Concentration:  NAAQS: 10,000 microgram/cubic meter (8hr average)
  • 20.
  • 21.  Large scale introduction of bus system will reduce large no of vehicles and save energy. However, in absence of progressive emission standards this will increase PM10 and SO2  In long-run a number of countermeasures would be necessary.  Tightening of emission standards is necessary but not sufficient: effective for SO2, PM10 and Nox but ineffective for reducing CO2.  Greater use of indigenously produced energy resources (electricity in this case)
  • 22.  Promoting public transportation, especially with those which high occupancy modes are essential for a number of factors  A package of countermeasures are necessary which only can address various priority issues such as PM10, congestion, energy saving, greater use of electricity and CO2  There should be synergies (coordination), not the conflicts, between local and global priorities in the Kathmandu Valley  Issues: Data quality (vehicle stock, operating factor, fuel efficiencies, emission factors)
  • 23.  http://www.iges.or.jplenlue  www.google.com.np  www.kathmandu.gov.np  http://ces.ioe.edu.np  www.dor.gov.np  http://www.environment-agency.gov.uk/