Initial assessment of some related socio-Economic parameters under the impacts of climate change at district 8 in Ho Chi Minh city
Results of AHP and LVI evaluation show that CC impacts on the studied parameters at
District 8 in HCMC can be divided into two groups of level from four criteria guided by the
ADB but also six criteria by the WB as tried in this study. The first impact level group includes
six main criteria whereas the second impact level group includes eighteen sub-criteria.
Calculated figures from both AHP (score 0.022, level 1) and LVI (0.073, which is the highest)
shows the strongest impacts of CC on public health, which well agrees with previous studies by
Pham [9] and Nguyen & Le [2]. Furthermore, this study points out a rather high level of CC
impacts on the study area, with an average LVI of 0.056. In addition, the results of AHP show
that the impact levels follow a decreasing order as: the first level group including energy, water
supply and drainage, transport, and public health; the second level group including land use and
wetland; the third level group including population and urban expansion; and at last the fourth
level group including GDP and agriculture.
Acknowledgements. This paper presents part of a research project funded by the Ho Chi Minh City’s
Department of Science and Technology that is much acknowledged. The authors also thank all colleagues
from ITE, who have contributed to this study
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Journal of Science and Technology 54 (2A) (2016) 214-221
INITIAL ASSESSMENT OF SOME RELATED SOCIO-ECONOMIC
PARAMETERS UNDER THE IMPACTS OF CLIMATE CHANGE
AT DISTRICT 8 IN HO CHI MINH CITY
Nguyen Phu Bao
1
, Tran Tuan Viet
1, *
, Nguyen Thi Minh Hoa
2
,
Nguyen Dinh Huan
3
, VoThi Yen
4
, Pham Hong Nhat
1
1
Institute for Tropicalization and Environment (ITE), 57A Truong Quoc Dung,
Phu Nhuan District, Ho Chi Minh City, Vietnam
2
University of Labour and Social Affairs, 1018 To Ky, District 12, Ho Chi Minh City, Vietnam
3
Industrial university of Ho Chi Minh City, 12 Nguyen Van Bao Street, Go Vap District,
Ho Chi Minh City, Vietnam
4
Ho Chi Minh University of Technology, 268 Ly Thuong Kiet, District 10, Ho Chi Minh City
*
Email: viet.vittep@gmail.com
Received: 1 April 2016; Accepted for publication: 15 June 2016
ABSTRACT
About 7.9 % of population is living in poverty at District 8, which is one of the most
vulnerable areas to climate change in Ho Chi Minh City (HCMC). The impacts of climate
change (CC) on some related socio-economic parameters at District 8 were assessed using
analytic hierarchy process (AHP) and livelihood vulnerability index (LVI). For this, four Asian
Development Bank’s criteria including public health, transport, energy, and water supply and
drainage (WSD) were used. In addition, however, six World Bank’s criteria including land use,
population, gross domestic product (GDP), urban expansion, agriculture and wetland were also
used just for initially trying whether or to what extent they can be useful for such downscaled
application. Results of this study show that the level of CC impacts on the residential areas is
rather high, with an average LVI of 0.056. In addition, the results of AHP shown that the impact
levels on the study fields are determined to follow a decreasing order as: first level group
including energy, water supply and drainage, transport, and public health (with total score 0.22);
the second level group including land use and wetland (with total score 0.14); the third level
group including population and urban expansion (with total score 0.1); and at last the fourth
level group including GDP and agriculture (with total score 0.09).
Keywords: climate change, analytic hierarchy process, district 8.
1. INTRODUCTION
The impacts of CC on the periurban areas of HCMC, including District 8, are increasingly
serious. There are 21 canals with total 106 km in length are winding through the District 8 (see
Initial Assessment of some related socio-economic parameters under the impacts of
215
Fig. 1), occupying 13 % of its total area [1]. Moreover, there are some other unfavourable
characteristics making the district become the most vulnerable area in HCMC, such as for
instance high elevation (from 0.5 to 2 m), high precipitation (average 1.743 mm), and high tide
peak (ranging between 1.36 and 1.46 m) etc [2]. Besides, about 7.9 % of population is living in
poverty at this district [1] and they are the most vulnerable people by CC impacts [3].
In this study, analytic hierarchy process (AHP) [4 - 6] was selected to assess CC impacts on
some related socio-economic parameters in the study area. The process is based mainly on four
ADB’s criteria including public health, transport, energy, and water supply and drainage [7]. In
addition, six WB’s criteria including land use, population, GDP, urban expansion, agriculture
and wetland [3] were also used just for initially trying whether or to what extent they can be
useful for such downscaled application.
2. MATERIALS AND METHODS
2.1. Study area
Six out of total sixteen wards, all administratively belong to District 8, were surveyed,
including wards No. 2, 3, 5, 13, 14 and 15 (Fig. 1).
Figure 1. Study area.
2.2. Survey methods
Ten households at each studied ward were requested to fill a 50-question-list sheet about
CC impacts on them. An environment staff in each ward people’s committee was asked to fill
another survey questionnaire about policy and other issues related to CC. Population and socio-
economic data were extracted from published sources [2]. In addition, three experts were asked
for consultation about CC impacts in HCMC and District 8.
2.3. Analytic hierarchy process
AHP is based on three rules including (1) making decision analyzing (priority set up), (2)
assessing the pairwise comparison, and (3) summarizing priority levels. The AHP is shown
below:
Step 1: Define the problem and determine the kind of knowledge sought.
Step 2: Define the elements and criteria.
Nguyen Phu Bao, et al.
216
Step 3: Determine the priority based on professional advices. The 1-to-9 scale of relative
importance was used (see table 1).
Step 4: Construct a set of pairwise comparison matrices.
Step 5: Compute the vector of criteria weights (w) for each level and each group as follow:
Once the matrix A is built, it is possible to derive from A the normalized pairwise
comparison matrix Anorm by making equal to 1 the sum of the entries on each column, i.e. each
entry aij of the matrix Anorm is computed as:
(1)
where, m is the number of elements.
Thus, the w (an m-dimensional column vector) is built by averaging the entries on each row
of Anorm, i.e.
. (2)
Table 1. Scale of relative importance [4 – 6].
Inten
sity of
importance
Definition Explanation
1 Equal importance Two activities contribute equally to the objective
3
Weak importance of one over
another
Experience and judgment slightly favour one activity
over another
5 Essential or strong importance
Experience and judgment strongly favour one activity
over another
7 Demonstrated importance
An activity is strongly favoured and its dominance
demonstrated in practice
9 Absolute importance
The evidence favouring one activity over another is
of the highest possible order of affirmation
2, 4, 6, 8
Intermediate values between
the two adjacent judgments
When compromise is needed
Step 6: Calculate the consistency ratio (CR). The CR value should be under 10 %, if not,
re-do step 3, 4 and 5:
(3)
where CI is Consistency Index and RI is Random Index (see Table 2).
Table2. Random index RI (with m ≤ 10) [4 - 6].
m 3 4 5 6 7 8 9 10
RI 0.58 0.9 1.12 1.24 1.32 1.41 1.45 1.49
Initial Assessment of some related socio-economic parameters under the impacts of
217
The CI is obtained by first computing the scalar λmax as the average of the consistency
vector ). Then
(4)
If ; and If re-assessment.
Step 7: Do step 3, 4, 5, 6 for all levels and groups.
Step 8: Compute the total weight and give comments.
2.4. Livelihood Vulnerability Index
LVI is calculated based on the following function [8]:
(5)
where LVId is LVI in each area d (or ward d); Md is main element/criterion in area d; and WMi is
weight of each main criterion, which is determined using the number of sub-criteria.
3. RESULTS AND DISCUSSION
3.1. AHP and LVI results
1. Energy, and
water supply and
drainage (WSD)
2. Transport
3. Public
health
4. Land use
and wetland
5. Population
and urban
expansion
6. GDP and
agriculture
1.1. Increase of
demand
1.2. Damage of
infrastructure
1.3. Changes in
supply
1.4. Salinization
of ground water
2.1. High flood
level
2.2. Effects on
human
activities
2.3. Duration
of flood
2.4. Damage of
vehicles
3.1. Arise and
spread of
diseases
3.2. Effects on
human health
3.3. Increase
of medical
treatment
costs
4.1. Loss of
land
4.2. Changes
in landuse
4.3. Salt
intrusion of
soil
5.1. Migration
5.2. Changes in
population
6.1. Decrease
of per capita
income
6.2. Changes in
production
structure
Figure 2. Prioritization of CC impacts at District 8.
Level 2
Climate change impacts at District 8
Level 1
ADB’s criteria WB’s criteria
Nguyen Phu Bao, et al.
218
The priority elements based on the ADB’s but also WB’s criteria were defined and
determined as shown in Fig. 2. Totally 7 weighting factor groups have been used in this step
including (1) one group for level 1 criteria (main criteria), and (2) six groups for level 2 criteria
(sub-criteria). Pairwise comparison matrix was built up based on the survey results as shown in
Table 3.
Calculations for pairwise comparison matrix and CR are shown in Step 5 and 6 above.
Results of vector of criterion weights is shown in Table 4 and CR in Table 5. Table 6 presents
vector of all criterion weights and LVI of each main criterion.
Table 3. Pairwise comparison matrix of main criteria (Level 1)
Criteria 1 2 3 4 5 6
1 1 1 1 2 3 2
2 1 1 1 2 3 2
3 1 1 1 2 3 2
4 0.500 0.500 0.500 1 3 2
5 0.333 0.333 0.333 0.3333 1 3
6 0.5 0.5 0.5 0.5 0.333 1
Total 4.333 4.333 4.333 7.833 13.333 12.000
Table 4. Vectors of criterion weights for level 1 group
Criterion 1 2 3 4 5 6 Average
1 0.23 0.23 0.23 0.26 0.23 0.17 0.22
2 0.23 0.23 0.23 0.26 0.23 0.17 0.22
3 0.23 0.23 0.23 0.26 0.23 0.17 0.22
4 0.12 0.12 0.12 0.13 0.23 0.17 0.14
5 0.08 0.08 0.08 0.04 0.08 0.25 0.10
6 0.12 0.12 0.12 0.06 0.03 0.08 0.09
Table 5. CR of main group and each criterion
Criterion 1 2 3 4 5 6
CR 0.026 7.4*10
-4
0 0.02 0 0
CR of main criteria 9.6*10
-3
Table 6. Vector of all criterion weights and LVI of each main criterion for assessing CC impacts at
District 8
Criteria
The vector of criteria
weights (w)
Priority LVI
1. Energy and WSD 0.22 1 0.055
1.1. Increase of demand 0.114 1
1.2. Damage of infrastructure 0.067 6
1.3. Changesin supply 0.025 11
1.4. Salinization of ground water 0.014 13
2. Transportation 0.22 1 0.055
Initial Assessment of some related socio-economic parameters under the impacts of
219
Criteria
The vector of criteria
weights (w)
Priority LVI
2.1. High flood level 0.073 4
2.2. Effects on human activities 0.073 4
2.3. Duration of flood 0.037 9
2.4. Damage of vehicles 0.037 8
3. Public health 0.22 1 0.073
3.1. Arise and spread of diseases 0.11 2
3.2. Effects on human health 0.055 7
3.3. Increase of medical treatment costs 0.055 7
4. Land use and wet land 0.14 2 0.046
4.1. Loss of land 0.08 3
4.2. Changes in land use 0.047 8
4.3. Salt intrusion of soil 0.014 13
5. Population and urban expansion 0.1 3 0.05
5.1. Migration 0.067 6
5.2. Changes in population 0.033 10
6. GDP and agriculture 0.09 4 0.045
6.1. Decrease of per capita income 0.068 5
6.2. Changes in production structure 0.022 12
Average LVI 0.056
3.2. Discussion
According the survey and AHP results, energy, WSD, transportation and public health are
the aspects that are most seriously impacted by CC in the study area. The vector of all those
criterion weights is 0.22 and they are the first priority. More specifically, the increase of energy
demand and WSD is impacted as the most, followed by arise and spread of diseases. Following
the first priority group are land use and wetland (total score 0.14); population and urban
expansion (total score 0.1); and GDP and agriculture (total score 0.09).
Figure 3. Spider chart of LVI of criterion groups caused by CC impacts in the study area.
Nguyen Phu Bao, et al.
220
The LVI of public health was highest (0.073), meaning that human health is seriously
impacted by CC in the study area. A similar result has been shown by Pham Hong Nhat et al. in
their study at HCMC in 2012 [9], which concluded, among other issues, that CC could cause
various hygienic and environmental problems. Results of LVI also show that the vulnerability
level of the remaining criterion groups follows a decreasing order as: (1) energy and WSD and
transportation (LVI = 0.055); (2) population and urban expansion (LVI = 0.050); (3) land use
and wet land (LVI = 0.046); and GDP and agriculture (LVI = 0.045) (see Fig. 3).
4. CONCLUSIONS
Results of AHP and LVI evaluation show that CC impacts on the studied parameters at
District 8 in HCMC can be divided into two groups of level from four criteria guided by the
ADB but also six criteria by the WB as tried in this study. The first impact level group includes
six main criteria whereas the second impact level group includes eighteen sub-criteria.
Calculated figures from both AHP (score 0.022, level 1) and LVI (0.073, which is the highest)
shows the strongest impacts of CC on public health, which well agrees with previous studies by
Pham [9] and Nguyen & Le [2]. Furthermore, this study points out a rather high level of CC
impacts on the study area, with an average LVI of 0.056. In addition, the results of AHP show
that the impact levels follow a decreasing order as: the first level group including energy, water
supply and drainage, transport, and public health; the second level group including land use and
wetland; the third level group including population and urban expansion; and at last the fourth
level group including GDP and agriculture.
Acknowledgements. This paper presents part of a research project funded by the Ho Chi Minh City’s
Department of Science and Technology that is much acknowledged. The authors also thank all colleagues
from ITE, who have contributed to this study.
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