|
GOAL 7: ENSURE ENVIRONMENTAL
SUSTAINABILITY
TARGET 9: Integrate
the principles of sustainable development into country policies and
programmes and reverse loss of environmental resources
|
INDICATORS
|
1990
|
1995
|
2000
|
2004
|
|
|
|
Area
under forests (percent)
|
37a
|
29b
|
|
|
|
|
Area
protected to maintain biological diversity (sq. kms)
|
10,948
|
20,077
|
20,077
|
28,585.7c
|
|
|
Energy
use per unit of GDP(TOE/mRs)d
|
34.8
|
29.0
|
28.4
|
29.6
|
|
|
Proportion
of people using wood as their main fuel (percent)e
|
75
|
67.74
|
67.74
|
69.1
|
|
|
Commercial
Energy/GDP (TOE/mRS)d
|
1.44
|
3.91
|
3.91
|
3.64
|
|
Sources: a MFSC 1988 (From aerial survey in
1978). b MFSC 1994. c DNPWC 2005.
d
MOF 2003/2004 and WECS 2003/2004. e CBS 1996 and 2004. NA=not available.
FORESTS AND
BIODIVERSITY
STATUS AND TRENDS
In Nepal,
29 percent of the total land area is covered by forest and 10.6 percent by
shrubs (MFSC 1994). Since the shrubs have the potential to turn into forest
areas, the total area under forests is 39.6 percent. The Forest Master Plan
(1988) which was based on the 1978 data showed 42 percent (37 percent forest
and 5 percent shrubs) of the total land covered by forest areas. The 1994
survey however, revealed that the country saw a decline in forest area,
compared to that in 1978 (MFSC 1988).
Over the past few decades, community-based forest resource
management (CBFRM) regimes whereby local and indigenous people are actively
involved in forest, land, and water resource management have shown good
results in maintaining forest cover and biodiversity richness, and experience
with pioneering instruments such as participatory community-based forest
management has been regionally acknowledged.
These participatory management regimes are intended to
directly or indirectly address the overarching national goals of poverty
reduction and sustainable development. For example, leasehold forestry regimes
are believed to be in the front line in the alleviation of poverty and in
restoring degraded land, while community forestry has also helped enhance
forest quality and coverage. Over the years, the number of community forest
user groups (CFUGs) involved in forest management
has increased (Figure 7.1). Recently however, the trend has declined because
the majority of the accessible forests in the hill and mountain areas have
been handed over and the government has restricted the handover of large blocks
of forest in the Terai. Several studies have
indicated positive impacts of community forestry, such as an increase in
biomass and plant abundance, and decrease in the number of open patches
inside the forests.
FIGURE 7.1: Pattern
of handing over of community forests to FUGs

Altogether, there are 19,961 CFUGS involved in managing
community forests throughout the country. Similarly, 2378 leasehold forest
groups are managing 9000 hectare of forestlands (DoF
2005 estimate). Among the NGOs, the FECOFUN has been playing a key role in
forest management and development. Different community groups involved in
community forestry, leasehold forestry, buffer zones management programmes,
and collaborative forest management are managing about 30 percent of the
country's total forest area and are moving towards self-reliance (MFSC 2005).
A watershed management programme is also contributing to
an increase in agricultural productivity through water, soil, and forest
conservation initiatives. Buffer zone management programmes have made
explicit efforts to link local livelihood needs with conservation needs in
and around protected areas through participatory measures to enhance people's
economic opportunities and reduce pressure in core areas. The current
challenge is to ensure the traditional rights of indigenous, poor, and
socially disadvantaged groups over natural resources in the buffer zones and
protected areas of Nepal.
Given the fragile physiography
of the country and the fact that the majority of the people live in rural
mountainous areas, the poverty-environment-health and vulnerability nexus is
very strong. The different community management regimes described above have
resulted in strengthened environmental governance and livelihood enhancement
through benefit sharing incentives along with enhanced access to resources.
Many rural families depend on ecotourism and on the trading of non-timber
forest products (NTFPs). Medicinal and aromatic plants
(MAPS) provide a source of income, medicines for primary health care, and
revenue for the national treasury.
Biodiversity conservation contains area of critical
importance for Nepal's
environment, because, it possesses a large diversity of flora and fauna, at
genetic, species, and ecosystems levels (MFSC 2002). This is due to the
climatic diversity in the vertical world of the Himalayas.
The area under protection in order to maintain biological
diversity has increased from 10,948 sq. km in 1990 to 28,585.7 sq. km in
2004. This comprises about 19.4 percent of the country's total area, and
represents all ecological zones. The protected area system includes 9
national parks (36 percent of the total protected areas), 3 wildlife
reserves, 3 conservation areas, 9 buffer zones, and one hunting reserve (MFSC
2002). Due to their outstanding ecosystem and landscapes, two of Nepal's
National Parks are listed as World Natural Heritage sites. Similarly, four
sites are designated as Ramsar sites.
Wetlands have been recognised as
one of the Nepal's
most important ecosystems and are important in terms of their ecological,
cultural, and economic value. Nepal
contains different types of wetlands but the largest coverage is by river
systems (53 percent) followed by paddy fields (43.6 percent) (MFSC 2002).
These ecosystems harbour 25 percent of Nepal's
biodiversity. About 172 species of the major wetland plants are listed (IUCN
1995). Out of 860 birds species found in Nepal, 193 are known to be
dependent on the wetlands (Bhandari 1998). Globally
significant wetland sites such as the Koshi Tappu Wildlife Reserve, Ghoda Ghodi Tal, Jagdishpur
Reservoir, and Bish Hazari
Tal are conserved and protected as per the specification of Ramsar sites.
Nepal
has a high degree of agricultural biodiversity (crop and animal genetic
resources) that is largely associated with the hills and mountains, where
variation in factors such as topography, slope, aspect, and altitude allow
for an enormous range of biological environment, climatic regimes, and varied
ecosystems. For example, out of more than 500 species of plans that are
edible, 200 are cultivated species (MFSC 2002).
SUPPORTIVE
ENVIRONMENT
Nepal
has a variety of enabling policies and the institutional environment to
ensure environmental sustainability, which is supported by external
development partners as well as NGOs. Furthermore, as explained above,
various CBFRM regimes have made significant contributions to enhancing
environmental sustainability as well as poverty reduction.
The Master Plan for the Forestry Sector (MPFS) provides a
twenty-one-year policy and planning framework for the forestry sector. The
Nepal Biodiversity Strategy (NBS 2002), reflects the
national commitment to adopt a more cohesive, strategic, and comprehensive
approach to conserving biodiversity and for the wise use of biological
resources. Among the six priority programmes under the NBS are national
forests, protected areas, wetlands, agro-biodiversity, rangelands, and
mountain biodiversity. In line with the NBS vision, a landscape-based
approach for biodiversity conservation is articulated in the PRSP (2002-2007)
to ensure coherence between productive and protected landscapes. The SDAN
(2003) provides a national vision for integrating the environment dimension
in the overall national planning framework. Several regulatory and policy
updates include the National Ecotourism Strategy (2004); the Buffer Zone
Regulations and Guidelines - updated (2004); legislation drafted to permit
the farming of common wildlife species, e.g. wild pigs, deer, and elephants
(2004); the National Wetland Policy (2003); and the Herbs and NTFP
Development Policy (2004).
Some specific outputs related to in-situ conservation
achieved in the recent past are as follows:
A National Register of plant species has
been established in the Department of Plant Resources of MFSC.
Biodiversity 'hot-spots' such as Badimalika, Phulchowki, Barandabhar and Tinjure-Milke-Jaljale
forests with rich genetic resources are legally protected and managed or are recognised for conservation.
A National Register of medicinal and
aromatic plants (MAPS) was updated in 2004.
A Central Biodiversity Information
(database) and Monitoring Centre was established at the
Department of National Parks and Wildlife Conservation.
Under the agro-biodiversity policy, in-situ and ex-situ
conservation strategies are being adopted by the National Seed Board of
Nepal, the Nepal Agricultural Research Council (NARC), and District
Agriculture Offices (DAO). Furthermore, a national database and inventory for
indigenous livestock has also been set up in NARC, along with a conservation
action plan. MFSC, with support from development partners, has been preparing
a Churia Area Programme Strategy (CAPS) which is
expected to contribute to the conservation of the fragile Churia
environment.
CHALLENGES
Despite the innovations on the policy and regulation
front, which includes salient strategies such as the SDAN and the NBS (2002),
progress in their implementation is poor as the mechanisms and capacities to
translate these strategies into actions are lacking. Without a due assessment
of institutional capacities and sectoral buy-in to translate policies into
action, results will remain weak. Since achieving environment outcomes
requires other non-environment related ministries to have the appropriate
polices, capacities, and regulations in place, this sort of inter-sectoral
mainstreaming is an aspect that requires stronger impetus.
Further challenges include conflicting provisions between
various policies and acts. For example, the Forestry Sector Policy (2000)
mentions the Collaborative Forest Management Strategy for managing the forest
block of the Terai and the Inner Terai. The Forest Act, on the other hand, contradictorily
stipulates that all national forests can be handed over to the FUGs. Although the LSGA has provided ownership and
authority over the forests in and around the local bodies, it contains
conflicting provisions, with altogether 23 Acts including Forest,
Environment, and National Park and Wildlife Conservation Acts.
Institutional bottlenecks such as centralised
decision making, the duplication of responsibilities, fragmented
responsibilities, and the lack of an integrated framework for coordination
among responsible agencies are notable. Similarly, equity in benefits sharing
and lack of inclusion in community management regimes of particularly
deprived ethnic communities are other key challenges.
While the primary aim of community forestry in terms of
maintenance of forest cover has been by and large achieved, there are second
generation issues such as good governance, livelihood strengthening, and
equity aspects which need to be strengthened. The Tenth Plan advocates on
these issues, in terms of redirecting the focus of the community forestry
programme and setting up mechanisms for fair and equitable benefit sharing of
genetic resources. The current challenge of the area is to reorient attention
to livelihood promotion, good governance, and sustainable forest management.
Similarly, policies related to national parks and
conservation areas have to tackle commercial interests in protected areas and
buffer zones. This underlines the belief that appropriate policies and robust
institutions to include local participation are necessary to affect conservation
outcomes. Furthermore, having a mechanism for trans-boundary partnership to
encompass ecosystem management and species conservation has long-term
significance.
Rapid demographic changes and weak land planning have
resulted in habitat loss. Political instability and insurgency has affected
programming and planning for conservation activities, while the lack of clear
scientific data on the impact of the decade long conflict on natural
resources makes future planning difficult. In the absence of locally-elected
structures, and in the presence of fragmented institutions, maintaining the
momentum of community-led regimes for resource management remains a challenge
due to issues of security and access.
ENERGY
STATUS AND TRENDS
After the initial decline during the first half of the
1990s, energy use per unit of GDP has slightly increased in the past few
years to about 30 TOE per million rupees and the commercial energy component
has increased steadily to about 3.64 TOE per million rupees of GDP (MOF 2004).
Around 40 percent of the population has access to electricity (CBS 2001) but
the gap between urban access (87 percent) and rural access (27 percent) is
very large (CBS 2004). Moreover, the Nepalese are the lowest per capita
electricity users in South Asia (around 70
kilowatt-hours per year).
The energy consumption in Nepal is still dominated by
traditional energy which makes up 87 percent of the total energy consumption
in 2004. Moreover, fuel wood accounts for almost 90 percent of the total
traditional energy of 7,397 TOE. Agricultural waste and dung are the other
types of traditional fuel being used in Nepal. The use of commercial
energy is also increasing rapidly, particularly petroleum products at 769
TOE, and electricity at 139 TOE (MOF 2004). The proportion of households
using wood as their main source of cooking fuel has increased slightly from
67.8 percent in 1995 to 69.1 percent in 2003, whereas the proportion of
people using cow dung and other resources such as straw as a source of fuel
has decreased from 25.8 percent to 15.7 percent during the same period. While
the proportion of people using liquid petroleum gas (LPG) saw a big jump from
0.99 percent in 1995 to 8.2 percent in 2004, the use of kerosene remains
almost unchanged (CBS, 1996 and 2004).
There is an urgent need to change the energy consumption
profile of Nepal,
as the majority of the population still depends heavily on fuel wood. This
represents a major challenge to environmental sustainability, because the
fuel wood is mostly extracted from forests, causing deforestation,
landslides, and erosion. The consumption of cleaner fuels, which stands at a
very low level at present, needs to be increased substantially.
In Nepal,
much emphasis has been placed on promoting alternative energy, especially
since the early 1990s. With respect to ensuring environmental sustainability,
the renewable energy initiatives have been contributing in three primary
ways.
Firstly, renewable energy such as biogas and improved
cooking stoves (ICS) reduces or reverses the forest depletion process. For
example, it is estimated that ICS can reduce fuel wood consumption in the
range of 25 percent to 40 percent (AEPC 2004). Secondly, the availability of
power in the rural areas opens up a host of new income and employment opportunities
through micro, small, and medium enterprises which divert or limit people who
otherwise would have been expanding cultivation on marginal land or would
continue selling fuel wood to earn their livelihoods. Thirdly, the renewable
energies have been facilitating information and communication technologies.
Various types of renewable energy technologies have seen a
steady expansion over the years. By the end of 2004, there were about 1500 pico- and micro-hydro electrification plants serving
approximately 80,000 households; over 800 turbine mills, serving thousands of
rural households (AEPC/CADEC 2004); more than 123,000 biogas plants installed
in 66 districts with more than 860,000 beneficiaries (BSP Nepal 2005); over
150,000 ICS built with even growing demand; and approximately 2000 improved
water mills installed. The trend from 2001 to 2004 in the use of these
different technologies indicates a sharp rise in the number of installations
of ICS, but a gentle decline in the others - micro-hydro plants, solar home
systems, and biogas technology.
SUPPORTING
ENVIRONMENT
The combination of grid-based and off-grid decentralised options, including both electricity and
non-electricity technologies, has resulted in significantly enhanced access
to modern sources of energy for rural people.
The breakthrough for the promotion of renewable energy
came with the Electricity Act (1992) which created an environment conducive
to community and private sector participation in hydropower development. The
Ninth Plan (1997-2002) put emphasis on these new energy technologies, which
was further enhanced by the 2001 Renewable Energy Subsidy Policy which
introduced subsidies for the construction and rehabilitation of
micro-hydropower, solar power, improved water mills, and biogas schemes. The
Tenth Plan has given top priority to the renewal energy sub-sector. It has
targeted to provide electricity to 12 percent of the rural population from
the alternative energy sources.
Currently, a new Rural Energy Policy is being prepared. Its
key objectives are the enhanced participation of communities and the private
sector in rural energy development as well as the promotion of modern energy
technologies in place of traditional biomass and fossil fuels.
Various multilateral and bilateral development agencies as
well as NGOs have been supporting the government's efforts in this sector,
with a particular emphasis on renewable energy sector in Nepal. Since 2000, under the
leadership of the Alternative Energy Promotion Centre (AEPC) established
under the Ministry of Environment, Science and Technology, various projects,
programmes and fund/subsidy flow have been streamlined.
Ensuring sustainable development of renewable energy
services
The key challenges in this area are as follows:
Continuity in commitment by the
government and external partners to the sector will determine the
sustainability of the programmes, as the financial resources required for the
installation of alternative energy systems have been identified to be
in the range of 2.3 billion rupees per annum.
policy and implementation gaps in the harmonisation of off- and on-grid rural electrification
programmes;
negative impact of the ongoing conflict
on the new installation as well as the operation of installed systems
in some cases; and
constraint on high quality installation
and repair and maintenance of renewable energy technologies by insufficient
availability of skilled human resources.
CHALLENGES
Despite some notable achievements in providing access to
modern energy services to Nepal's
rural population, the sector still faces major challenges. On top of the
problems such as leakage of electricity which is estimated to be more than 20
percent and loss of energy and poor cost recovery, the three key challenges
to the energy sector in the country are the following.
Limited access to
renewable energy services of the poor, and particularly in remote areas
Major challenges that have hindered access are:
low
affordability and lack of a financial support system for the poor - capital
intensive technologies like biogas and solar PV have mainly reached the rural
middle class;
lack
of access to information about benefits and policies;
lack
of adequate technical /managerial support; and
lack
of awareness among the general public about the negative health impacts of
indoor air pollution and other environmental and social impacts of continued
use of conventional energy.
Productive end use
of renewable energy in rural areas
The key challenges include:
small
local market, viz. low purchasing power of local people to consume the goods
produced using alternative energy;
inadequate transportation facility for
movement of goods;
lack of access to information
about the production technology to utilise local
energy resources and market information;
lack of adequate financial support
systems; and
lack of managerial, technical, and
financial skills/ ex
TARGET 10: Halve,
by 2015, the proportion of people without sustainable access to safe drinking
water
|
INDICATORS
|
1990
|
1995b
|
2000c
|
2005d
|
2015
|
|
Target
|
Will development goal be
reached?
|
|
Proportion of population with sustainable access to an improved water source11
|
46a
|
70
|
73
|
81
|
73
|
Likely
|
|
Rural
|
43a
|
68
|
71
|
79
|
72
|
|
Urban
|
90a
|
96
|
86
|
93
|
95
|
|
Proportion
of population with sustainable access to improved sanitation
|
6e
|
22
|
30
|
39
|
53
|
|
Rural
|
3e
|
18
|
25
|
30
|
52
|
|
Urban
|
34e
|
67
|
80
|
81
|
67
|
Sources: a Nepal Family
Health Survey 1991. b CBS 1996. c MoH, NDHS 2001. d
CBS 2003/04.
e Nepal
State of Sanitation Report (Colombo Resolution 1990)
STATUS AND TRENDS
While the MDG target aims to increase "sustainable
access to safe drinking water," this is difficult to assess, due to wide
variations and definitions in water supply. The available data was derived
from various surveys which used different criteria. If 'access to drinking
water' is examined, Nepal has been making a rapid progress in this area, as
presently 81 percent of the total population has access to improved water
sources, compared to only 46 percent in 1990.
Given the importance of adequate water supply and
sanitation, there has been significant progress in a relatively short space
of time. During the Water Supply and Sanitation Decade (1981-1990), for
example, the population with access to a protected water source rose to 36.7
percent. However, according to a recent survey, out of the 5000 water points
in 22 hill districts, only 21 percent are functioning as designed, 56 percent
require major repair, and 21 percent need complete rehabilitation (DWSS/WAN
2003). This suggests the dimension of the problems of the water supply system
and warrants scrutiny.
Overall, sanitation coverage increased substantially from
6 percent in 1990. The NLSS 2003/ 04, the most recent survey data available,
found that the percentage of households with access to toilets was 39
percent. With all the sectoral players participating, National Sanitation
Week alone prompted the construction of 60,000 toilets within a short period
(DWSS 2004).
However, it must be noted that significant disparities exist
in access to water and sanitation, in spite of the rapid expansion of the
last fifteen years. In Nepal,
the richest quintile is 13 times more likely to have piped water in their
homes than the poorest quintile (39 percent vs. 3 percent), and are nearly eight
times more likely to have improved sanitation (79 percent vs. 10 percent)
(UNICEF 2005, based on NLSS 2003/04). In addition, there is a considerable
degree of geographical disparity, as shown in Map 7.1. It should also be
noted that in Nepal,
especially in urban areas, having access to improved water sources does not
mean that water is always available in sufficient quantity, as many
households do not receive a regular supply, particularly during the dry
season (UNICEF 2005). The reliability and service level elements of water
access need to be carefully assessed.
Over the years, the gap between the urban and rural areas
has been narrowed in terms of access to water and sanitation coverage. For
water supply, the rural coverage has been showing steady progress and
reaching the Target is likely. On the other hand, progress in urban areas has
stagnated, due to the rapid population increase in urban centres
and the inability of the urban system to keep up with growing demand. For
sanitation coverage, most households in urban areas have toilets, and
progress has been on track. In rural areas, coverage is still low and
accelerated efforts are needed to meet the MDG target.
As for water quality, the national standards for assessing
water supply, including its safety and sustainability, have now been
introduced. By these standards, 5 percent of the population currently has
access to a high-quality water supply, 20 percent to a good quality water
supply, with 75 percent relying on a basic-quality one (DWSS 1997). Nevertheless,
many so-called 'safe' water sources may be contaminated through the seepage
of wastewater around the outlet, contamination at the source, or
contamination during transmission. According to a survey by the Department of
Water Supply and Sewerage, 55 percent of tubewells
in 20 Terai districts were microbiologically
contaminated (DWSS 2002).
Arsenic contamination, which occurs naturally in the
groundwater of the Terai, has also been a growing
concern in many Terai districts. A recent survey
has indicated arsenic contamination even in the Kathmandu Valley. The National Arsenic Steering
Committee reported that 15 percent of the 339,515 tube wells have arsenic
levels above the WHO standard and 3 percent above the Nepal standard. Even by the Nepal
standard, about 300,000 people are using arsenic-contaminated water. By WHO
standards, the figure for the number using arsenic-contaminated water is as
high as 1.5 million. If bacterial contamination were considered, the
population using unsafe water would be far greater (UNICEF 2005). Thus, if
the strict definition of access to safe drinking water were applied, Nepal's
coverage could be considerably lower.
As for wastewater, thus far, most of the institutional
arrangements over wastewater management have been focused in the Kathmandu
Valley. The valley's
wastewater management infrastructure consists of treatment plants, pump
stations, collector mains, and interceptors. Due to inadequate management,
most of these plants and equipment are either out of operation or are only
partially operational. Four out of the five treatment plants in the valley
are out of operation. As a consequence, raw sewage is being discharged
directly into water courses polluting them, damaging the environment, and
increasing the risk of the spread of disease.
Solid waste makes up 83 percent of the total waste
generated in the country, of which agricultural waste is 11 percent and
industrial waste 6 percent. Increasingly, solid waste and plastic litter are
a visible environmental problem. Urban households generate the most solid
waste in the country, at 0.48 kg per capita per day. In 1999, three million
urban residents of 58 municipalities generated a total 426,486 tonnes of waste, out of which Kathmandu's share
was 29 percent (HMG/ JICA 2004). Medical waste alone in the valley is
generated at the rate of 1.7 kg per day per bed, out of which infectious
waste is generated at a rate of up 0.48 kg per hospital bed per day. Thus,
the valley's estimated 3905 hospital beds generate up to 1,312 kg of
infectious waste per day. Most of this waste is either dumped as ordinary
garbage or burned in ordinary kilns (ENPHO 2000).
SUPPORTIVE
ENVIRONMENT
The aim of the National Water Plan (2002-2017) was to meet
the increasing demand for drinking water and for sanitation. According to
this plan, by 2017 the entire population will have access to a water supply,
of which 27 percent will have medium- to high- quality water supply, while a
full 100 percent will have access to sanitation facilities. The plan also addresses
urban sewerage and wastewater treatment related to drinking water, as well as
sanitation.
The revised Rural Water Supply and Sanitation National
Policy 2004 clearly indicates that the government and local bodies will
regulate, monitor, and facilitate the implementation of rural water and
sanitation plans and programmes. The role of the line agencies is to provide
policy guidance and technical back-up while NGOs will assist community user
committees in formulating and implementing projects, managing funds, carrying
out pilot schemes, and recommending policy and programme modifications.
The PRSP (2002-2007) sees the problem of final disposal as
the major challenge in solid waste management, especially in the Kathmandu
Valley. It also emphasises infrastructure development as the long-term
solution. A major initiative, the Melamchi Water
Supply Project, is aimed at meeting the medium-term needs for water supply of
the Kathmandu
Valley.
The lead agency in the water and sanitation sector is the
Department of Water Supply and Sewerage (DWSS) under the Ministry of Physical
Planning and Works. The Department directly executes large rural water supply
schemes funded directly by the government and the Asian Development Bank
(ADB) under the Fourth Rural Water Supply and Sanitation Project. They also
execute urban schemes under the ADB-funded
Small Town
Water Supply Project. The World Bank also funds rural water supply projects
through the Rural Water Supply and Sanitation Fund Development Board
(RWSSFDB) and more recently it has been playing key role in providing water
supply and sanitation services in the rural areas. The Ministries of Health,
Education and Local Development are also involved in efforts complementing
those of DWSS. Some initiatives include putting the subject of sanitation
into secondary school courses and introducing environmental education at the
primary level. Grants have also been provided to village development
committees for drinking water and sanitation work, resulting in some
promising local initiatives (Box
7.3).
DWSS is also the lead agency for sanitation. The National
Committee for Sanitation Action (NCSA) coordinates the sanitation activities
of the numerous agencies working in the sector, advises on policy and
strategic issues, and plans and manages the activities under the National
Sanitation Action Week. An example of the collaborative effort promoted by
the NCSA to develop a strategy to accelerate latrine coverage is indicated in
Box 7.4.
Various HMG/N organisations and
institutions are involved in solid waste management (SWM) at the policy and organisational level. The Solid Waste Management and
Resource Mobilisation Centre supports the Ministry
of Local Development to: (a) develop appropriate legislation; (b) develop
environmental guidelines; (c) deal with landfill site development issues; (d)
provide financial support wherever appropriate in all aspects of solid waste
management; (e) provide technical support to municipalities; (f) enhance the
capabilities of municipalities; and (g) act as a link between the ministry
and municipal bodies. Local bodies such as the municipalities assume the core
operational responsibility of managing solid waste in their own
jurisdictions.
CHALLENGES
The increasing demand for water for drinking, industry,
and irrigation have outstripped the improvement rates in water supply and
sanitation facilities. As a result, major towns and cities in the hills are
facing acute shortages. The CBS study (2005) carried out in Kathmandu shows that 59 percent of the surveyed
households do not have an adequate water supply from the piped water line,
and on average, water is available only four days a week. In many cases,
water quality deteriorated due to a lack of treatment plants and poor supply
network. There are no proper sewerage networks in the rural areas or even in
the municipalities except in core areas of the municipalities in the Kathmandu
Valley. Existing as
well as newly-emerging towns are likely to face a scarcity in drinking water
and sanitation.
Ensuring water quality is also a major challenge in Nepal.
As indicated earlier, because of source contamination, even piped drinking
water is unsafe in many areas almost throughout the year. Nationally, 30
percent of the households reported incidences of diarrhoea,
dysentery, jaundice, and typhoid or cholera. Among children under five years
of age, the prevalence of diarrhoea was 20.4 (MoH/New ERA ORC MACRO 2002). Nearly 3 percent of the
groundwater supply of drinking water in the Terai
is contaminated with unacceptable levels of arsenic and some contamination
has been found in groundwater in Kathmandu
as well. Even if the water source is not contaminated, drinking water is
often contaminated at the household level, for example because unclean con
tamers are used or water becomes contaminated during
storage. Improving the management and treatment of drinking water at the
household level is an appropriate option for the country.
Kathmandu
lacks a planned wastewater management infrastructure. The CBS study (2005)
also states that two-thirds of the households in the Kathmandu Valley have access to a sewage
facility. Almost all domestic wastewater and industrial wastes are discharged
directly into the Bagmati and Bishnumati
rivers without treatment throughout the year. Essentially, the rivers are
turned into open sewers during the dry season. Sewerage service coverage of
these plants is limited, considering the population of Kathmandu, and its operation cost is high
and difficult to sustain.
While experience with rural water supply indicates that
community participation helps to make drinking water and sanitation
initiatives cost effective, the situation in the urban areas has been almost
the reverse. The water supply systems in the urban areas have not even been
able to recover the costs. In addition, they suffer from both an inefficient
distribution system and a high level of leakage.
Sanitation has always been a low priority programme area,
never receiving the attention and resources to make any significant
improvements, although there are indications this is changing. During the
past two to three years the NCSA, under the leadership of DWSS, has been
effective in raising awareness about the importance of sanitation and
facilitating a collaborative effort among a large number of agencies.
Promoting sanitation through schools is an emerging strategy that has the
potential to significantly increase coverage. The major challenge is to
convince the various agencies to adopt a common approach and allocate
adequate resources to reach the MDG targets.
The MDG
Needs Assessment Study has identified the intervention packages that would
enable the fulfilment of the MDG. The study
estimated a resource gap of Rs. 137.398 billion (US $1962.83 million) in
investment from 2005 to 2015 for drinking water and sanitation. It is certain
that drinking water will require the largest amount of resources. At the same
time, the stress will have to be not only on increasing coverage but also on
improving the quality of coverage. The solid waste management and sanitation
sub-sector has not received adequate attention, in resources and
institutional reforms, as it is overshadowed by the needs of water supply.____________________________________
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