Brick Kilnchlorofluorocarbons (HCFC–22) as ozone depletingsubstances (ODS). The consumption of these twosubstances was 30 tons and 23 tons, respectively(NBSM and UNEP undated). The country does notproduce any ODS itself—all these substances areimported. The annual per capita ODS consumptionin Nepal in 1999 was 0.0013 kg. The regulatorymeasures developed to address the problem aredescribed in a later section.Natural Sources of Air PollutionNatural sources of air pollution include suchthings as volcanic eruption, forest fires, pollens fromvegetation, and salt particles from sea spray. Forestfires occur annually in all the major physiographicand climatic regions of Nepal, including the Terai andBhabar, the Siwaliks or the inner Terai, the MiddleMountains, and the High Mountains, althoughreliable statistics are not available. Pollen grains areanother natural contaminant associated with healthproblems such as allergies. Many people suffer fromasthma or hay fever although the symptomsdisappear at the end of the pollen season—someeven develop bronchitis, bronchial asthma, anddermatitis. Suspended dust from roads is also highlyvisible in Nepal, adding to the suspended particleload in the air.Impact of Air PollutionAlthough air pollution has become a visible environmentalproblem in the last decade, only limited dataare available to evaluate its magnitude and impact.The health impact of indoor and outdoor airpollution can be assessed by the increase in thenumber of patients suffering from diseases related toair pollution. Health effects range from minorirritation of eyes and the upper respiratory system tochronic respiratory disease, heart disease, lungcancer, and death. Air pollution has been shown toB.B. Pradhancause acute respiratory infections in children andchronic bronchitis in adults. It has also been shownto worsen the condition of people with pre-existingheart or lung disease. Among asthmatics, airpollution has been shown to aggravate the frequencyand severity of attacks. Both short-term and longtermexposures have also been linked to prematuremortality and reduced life expectancy (Mishra 2003).The health impact of air pollution depends onthe pollutant type, its concentration in the air, lengthof exposure, other pollutants in the air, and individualsusceptibility. Different people are affected by airpollution in different ways. Poor people,undernourished people, the very young and very old,and people with pre-existing respiratory disease andother ill health are more at risk (Mishra 2003).Exposure to particles can lead to a variety ofserious health problems. Fine particles pose thegreatest problems because they can get deep intothe lungs and some fine particles into thebloodstream. Long-term exposure to particulatematter shows decreased lung function, chronicbronchitis, premature deaths, and heart attacks. Nolong-term epidemiological studies have beenconducted in Nepal, but a few studies haveconducted preliminary medical examinations of agroup of exposed people or used dose-responserelationships developed elsewhere.According to the data published by the thenMinistry of Health (now Ministry of Health andPopulation), among patients visiting the majorhospital (DOHS 2003), ARI ranks as the third-highestcause of morbidity in Nepal after diarrhea, affecting3.13% of the total population (this document,Chapter 2, Table 2.<strong>18</strong>). Chronic bronchitis falls at theeighth position.Pandey et al. (1987) examined 240 rural childrenunder 2 years of age for 6 months and found asignificant relationship between the number of hoursspent near the fire (as reported by the mother) andthe incidence of moderate and severe cases of ARI.The study suggested that indoor air pollution is animportant risk factor for ARI. A 1971 review of thecases of discharges from ten hospitals with acombined capacity of 265 beds revealed that ARIaccounted for 32% of mortality for infants less than 1year and 11% for children aged 1–4 (WINROCK2004).COPD is another major risk, especially amongwomen, and has been strongly associated withsmoke exposure from cooking on open biomassstoves. In rural Nepal, nearly 15% of non-smokingwomen 20 years and older had chronic bronchitis(WINROCK 2004), a high rate for non-smokers.Similar cases are observed in the urban centerswhere outdoor air pollution is soaring. A study by the90 Environment Assessment of Nepal : Emerging Issues and Challenges
World Bank in 1990 estimated impacts on mortalityand morbidity due to PM10 levels. The study estimatedthat Kathmandu’s PM10 levels resulted in 84 casesof excess mortality, 506 cases of chronic bronchitis,4,847 cases of bronchitis in children, and <strong>18</strong>,863asthma attacks per year. Overall, Kathmandu’sresidents experienced over 1.5 million respiratorysymptom days per year (Shah and Nagpal 1997).An analysis of the records of 369 COPD patientsand 315 control patients admitted to Patan Hospitalfrom <strong>April</strong> 1992 to <strong>April</strong> 1994 showed that the odds ofhaving COPD are 1.96 times higher for KathmanduValley residents compared with outside residents.The study also stated that over the past decade theproportion of COPD patients had increased morethan fourfold and that COPD was the number onekiller of adult patients in the hospital (CEN andENPHO 2003).The records from three major hospitals inKathmandu indicate that the number of COPDpatients admitted to hospitals, as well as the numberof COPD patients as a percentage of all patients, hasincreased significantly in the last ten years. Hospitalrecords also indicate that the number of COPDpatients is highest in the dry winter months, when airpollution in Kathmandu is at its peak (Figure 7.12).Vehicular pollution and suspended dust from poorlymaintained roads are the major causes for the poorair quality in urban centers.Another observable impact is on visibility.Atmospheric data obtained from Kathmandu airportfrom 1970 onwards shows a substantial decrease invisibility in the Valley since 1980. The trend towardsreduced visibility in the Valley has been quitedramatic for the months November–March, andparticularly for December–February. The number ofdays with good visibility (>8,000 m) at 11:45 amdecreased in the winter months from more than 25Figure 7.12: Air Pollution Level in Kathmandu andIncidence of Chronic Destructive Pulmonary Disease(COPD) Patients as a Percentage of All Patientsdays/month in 1970 to 5 days/month in 1992. By 1997,the number of days per month in December–February with good visibility at noon approachedzero (Sapkota et al. 1997).The impacts of air pollution are felt not only onhealth but also on vegetation and in corrosiondamage to buildings and monuments. Air pollutioncan inflict significant damage on local vegetation.The information collated by Regional Air Pollution inDeveloping Countries during the initial phase of theCrops and Forests Project has clearly shown that inmany developing countries, and particularly in partsof Asia, crop yields and forest productivity are beingseverely affected by local ambient air pollutantconcentrations. In the context of South Asia, there isa strong linkage between monsoon activity andagricultural productivity. In the last decade, Nepaland the Indo-Gangetic plains of India experiencedsevere sky overcast during winter, affecting majorwinter crops like potato, oilseeds, pulses, and onion.Yield reduction in 1997/98 ranged from 11% to 38%compared with the average of the preceeding 10years. The precise reasons for this, however, are notyet clear. Frequent occurrence of cold waves and fogmixed with dust particles in the atmosphere could bethe cause. Likewise, reduction of solar radiationcould be the explanation. Aerosols can directly alterthe hydrological cycle by suppressing evaporationand rainfall. With respect to agricultural changes, itcan directly impact productivity by shadingvegetation from solar radiation; and indirectlythrough induced changes in temperatures and thehydrological cycle (UNEP and C4 2002).Climate and Climate ChangeNepal’s ClimateThe climate in Nepal varies from tropical to arcticwithin the 200 km span from south to north. Much ofNepal falls within the monsoon region, with regionalclimate variations largely being a function ofelevation. National mean temperatures hover around15°C, and increase from north to south with theexception of the mountain valleys. Average rainfall is1,500 mm, with rainfall increasing from west to east.The northwest corner has the least rainfall, situatedas it is in the rain shadow of the Himalayas. Rainfallalso varies by altitude—areas over 3,000 mexperience a lot of drizzle, while heavy downpoursare common below 2,000 m. Although annual rainfallis abundant, its distribution is of great concern.Flooding is frequent in the monsoon season duringsummer, while droughts are not uncommon incertain regions in other parts of the year.Data Source: Limbu (2005)Chapter 7: Air Pollution and Climate Change91
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About the OrganisationsAsian Develo
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© 2006 International Centre for In
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AcknowledgementsWe would like to ex
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PM2.5PAHRSSAARCSACEPSEASO 2TSPUKUND
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Chapter 6: Energy Resources 65Intro
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List of FiguresFigure 2.1: People a
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Table 6.1: Energy Consumption and P
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forests are also used for infrastru
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as data gathered by different agenc
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Table 2.1: Population Growth Rates
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mortality rates for rural and urban
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Agglomeration village in the centra
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soil erosion, and depletion of wate
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provision remains inadequate becaus
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Malnutrition remains a serious obst
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Table 2.24: Existing and Projected
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Table 2.28: Income Poverty Indicato
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Table 2.31: Change in Employment St
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In 2004, the average annual househo
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Mountain areas have the most food i
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Schaffner, U. 1987. “Road Constru
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Table 3.1: Agricultural Economic De
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Table 3.4: Estimated Soil Erosion R
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B. PradhanImpacts of land degradati
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Carson, B. 1985. “Erosion and Sed
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. Cultural Heritage8. Convention fo
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Appendix 9.3: Some Prominent Enviro
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Some funding arrangements made by t
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(NARDF 2004) for a period of 1 to 3
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Table 10.2: Annual Income and Expen
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Table 10.4: Users’ Share in Benef
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From Hands Around Everest bookFrom
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Table 10.8: Subsidy Rate for Biogas
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microorganism communities and the n
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subsidies (Mason 1996). All these a
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addressed only part of the problem.
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historical practice of community-ma
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moved or relocated. The fact that s
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Kathmandu Valley and receives a lar
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cooperative ventures provided neith
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further poaching has not been repor
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http://www.pugwash.org/reports/pac/
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United Nations. 2003. World Populat
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how other countries with substantia
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(i) Broad-based and sustainable eco
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Although progress is encouraging, m
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Nepal’s Changing Pattern of Trade
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Table 12.2: Trade/ GDP RatiosFY1981
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Table 12.5: Percentage Share of Maj
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well as other provisions in specifi
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Future Implications for NepalIncrea
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International Trade Forum (ITN). 20
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- Gross domestic product per unit e
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Time Series InformationGenerally tw
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Table 13.1a: Different Datasets Col
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elevant due to its multidisciplinar
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Figure 13.6: Examples of Applicatio
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Judith DobmannThere are many source
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sustainable livelihoods requires an
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and haphazard. Population pressures
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issue. These deficiencies stem from
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population must be assessed. MOEST
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Appendix 14.1: List of Key Environm
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(vii) The EIA report approving agen
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Goal 1: Eradicate extreme poverty a
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Nepal’s Progress Towards the MDGs
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Goal 4: Reduce child mortalityReduc