Protection, development and recovery of forest are vital strategies for
developing countries to achieve sustainable development. Since the 1990s, Vietnam
has been interested in restoring forests in the face of severe forest degradation.
Understanding the relationship between forest cover and economic development is a
challenge for researchers and policymakers in Vietnam. Based on the framework of
economic theory and practice in Vietnam, the study used a multivariate linear
regression model to assess the economic factors affecting forest cover. The study uses
the secondary data period 1990-2017 in Vietnam. Research results confirmed: Rural
population and GDP per capita (Low / High economic development level) have an
impact on forest cover and these relationships following the shape of Kuznets
environmental curves
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THE RELATIONSHIP BETWEEN FOREST RESTORATION
AND ECONOMIC DEVELOPMENT IN VIETNAM: EVIDENCE
AND POLICY IMPLICATION
Luu Tien Dung (PhD)
Lac Hong University
Email: dunglt@lhu.edu.vn
Tran Hoang Minh (MBA)
Lac Hong University
Email: minhth@lhu.edu.vn
Abstract
Protection, development and recovery of forest are vital strategies for
developing countries to achieve sustainable development. Since the 1990s, Vietnam
has been interested in restoring forests in the face of severe forest degradation.
Understanding the relationship between forest cover and economic development is a
challenge for researchers and policymakers in Vietnam. Based on the framework of
economic theory and practice in Vietnam, the study used a multivariate linear
regression model to assess the economic factors affecting forest cover. The study uses
the secondary data period 1990-2017 in Vietnam. Research results confirmed: Rural
population and GDP per capita (Low / High economic development level) have an
impact on forest cover and these relationships following the shape of Kuznets
environmental curves.
Keywords: Forest degradation; Forest restoration; Economic development;
The environmental Kuznets curve (EKC).
1. Introduction
Belov (1976), The forest system on the earth is providing 37 billion tons of
biomass (70%), its flora produces oxygen to serve for the humans, animals and insects
(44% oxygen from forest trees). Each year a person needs 4.000 kilograms of oxygen
to correspond with the amount of oxygen which produced by 1.000 to 3.000 square
meters of trees in a year. Forests regulate the global climate by significantly reducing
the heat from the sun to the earth due to the forest canopy cover is very large and
more useful than types of land using, especially the very important role of forests in
maintaining the carbon cycle on the earth by which it directly affects to the global
climate changes. Therefore, the existence of forest ecosystems plays a significant role
to against the global warming and regulate the climate. The world experience shows
that the maintaining, developing and protecting forests have the relationship with
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economic development levels. The study focuses in: i) Theoretical and experimental
basis of the relationship between forest restoration and economic development levels; ii)
The Vietnam’s environmental Kuznets curves are evidence for the forest degradation
with the relationship between forest degradation and the economic development levels;
and iii) and policy implications for the forest development in Vietnam.
2. Theoretical and experimental basis of forest restoration and economic
development
Kuznets (1955) discussed: The Gini index and the economic development
(GDP/person) have a relation like the U-inverted in long-term. Figure 1 show that: in
the first-stage, the economic development levels are still low, the GDP per capita is
increased and the Gini index is also increased. When the economic development
levels will be increased, the Gini will be lowdown.
Fig. 1. The Kuznets curve
According to Yandle, Vijayaraghavan and Bhattarai (2002), the environmental
Kuznets curve (EKC) was popularly using in the world from 1991.
Fig. 2. The environmental Kuznets curve
GDP/person
Gini index
The environment
pollution
GDP/person
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The environmental pollution status could be measured by the level of air-
pollution or water-pollution. When the economic development levels are low, the
GDP is high, the environmental pollution status is high; but when the economic
development levels will be more increasing, the environmental pollution status will
be decreased due to the technology level and high-tech products are more and more
produced and replaced for traditional fuel products.
Samuelson formed theoretical basis and applied the Kuznets curve into forest
degradation and forest restoration.
In the Figure 3a, the status of forest degradation and the economic
development level had the relationship in same direction but it liked the U-shaped
invertation. People used forest products in the early stages of development, but after
the per capita income is increasing, forest products are replaced by some other
substitutes that do not harm the forest. And, the higher growth population and
agricultural expansion to result in deforestation and this trend can be stopped through
a depth agricultural development and build appropriate political and social
institutions (Laurance, 2007; Rudel & et al., 2005; Culas, 2007). In the rural areas of
developing countries, fuel fuels, especially firewood from forests was used wisely
(Balat & Ayar, 2005). As the higher income, households change from using dirty
fuels to clean fuels (Alam, Sathaye, Barnes, 1998; Davis, 1998; Leach, 1992).
Therefore, the using of fuel wood was assumed that it was decreased with highly
increased per capita income by replacing it from alternative energy sources such as
electricity and gas. The amount of wood used in furniture, buildings or construction
would be reduced due to the alternative materials for wood (Barbier & et al., 2010;
Forest degradation
GDP/người
Forest restoration
GDP/person
Fig. 3a. The Kuznets curve of forest
degradation
Fig. 3b. The Kuznets curve of forest
restoration
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Lambin & Meyfroidt, 2010). Moreover, the governments are conducting reforestation
programs and the highly increased per capita income, education and environmental
awareness also will be enrich, all that will help to reduce deforestation rates. So, if
selecting forest rehabilitation targets (forest coverage rate) replace forest degradation
targets in the model of the U-shaped invertation, Figure 3b will the relationship
between the forest restoration and the economic development like the U-shape.
Shafik and Bandyopadhyay (1992), conducted an empirical research on the
inverted U-shaped relationship in 1992. Koop and Tole (1999) analyzed the case
of the developing nations’ forest degradation, it showed an economy with more
inequality, the forest degradation would be more serious. Basing on database of
66 nations, in the period of 1962 - 1986, Winslow (2005) showed that the forest
degradation had a correlative relationship with the economic development as the
Kuznets curve. In Mather (2007), the Asian countries’ economic growth affected
to the forest degradation. According to Bhattarai and Hammig (2001), Ewers
(2006), Scrieciu (2007), the forest degradation and the economic development had
a relationship in the U-shaped invertation in developing countries. Results of the
Miah et al. (2011) also showed the Bangladesh’s forest degradation in a
relationship with the economic development with the U-shaped invertation. To
Jesús et al. (2017), found evidence that factors affected to the forest restoration,
included: per capita income, per capita income with the high economic
development status, the economic growth rate, percentage of rural population and
the population growth rate.
3. Research model in Vietnam
To base on the theories, experimental studies in the world and some evidence
in Vietnam, we chose model of several following factors to affect the forest
restoration status:
Fig. 4. Research model
FOREST RESTORATION Income/person
(When the economic
development levels
are low.)
Income/person
(When the economic
development levels
are high.)
The rural
population
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Table 1: Variables definition in the model
Order Name Definition Measurement
Expecte
d signs
I Dependent variables
FC (Rate of forest cover)
Forest coverage rate
Acreage of forest coverage/
acreage of natural soil (%)
II Independent variables
1 YP (GDP per capita) GDP/person Price of 2010 -/+
2
YPS (GDP per capita)
square
(GDP/person) square
Assuming GDP/person in a high
economic development level
+
3
PR (Percentage of rural
population)
Percentage of rural
population
% -
4
GP (Growth of
population)
Growth of population % -
The study used model of multivariate linear regression and database in 27
years (1990 - 2017). The database has processed from sources of General Statistics
Office (1990 - 2017); World Bank (2010 - 2018); Annual reports on socio-economic
situation of General Statistics Office (1990 - 2018); Some relation studies to the forest
degradation in Vietnam (1990 - 2020).
4. Results and discussions
4.1. Trends of forest restoration
With effective policies in protection and forest restoration by the Government
of Vietnam through periods, especially the policy of greening bare land - bare hills
from 1991, the forest restoration achieved amazing achievements.
In the Figure 5, the year 1943, the forest coverage rate was 43%, and it was
33.6% in 1976. From 1976 to 1993, Vietnam was one of the nations has the serious
forest degradation in world (the forest coverage rate was 26.1% in 1993). In the
Figure 5, the line went-down with a serious slope down. From 1994 to 2017, the forest
coverage rate went-up, to the year 2017, the forest coverage rate was 41%, nearly
equal the year of 1943.
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Fig. 5. The status of forest coverage in Vietnam (1943 - 2020)
Source: Authors processed from sources of General Statistics Office and some
relation studies in Vietnam.
When we compared the Vietnam’s forest coverage rate with some nations in
the region, fig. 6 showed that in 25 years ago, Vietnam and China are increasing
significantly the proportion of forest area/natural soil area, while other nations in the
region, this rate slowly decreased (Indonesia, Thailand, Cambodia) and Laos,
Malaysia, Philippines are going-up in the recent years. That affirmed Vietnam
becomes one of the region's top countries in paying attention to economic
development associated with sustainable development.
Fig. 6. Trends of changing in the forest acreage rate/ the acreage of natural soil
in some countries 1990 - 2015 (%)
Source: World Bank (WB, 2018)
43.0
33.8
30.2 30.0
27.827.928.0
26.1
27.0
28.2
29.0
29.5
32.0
33.2
34.4
35.0
35.836.0
36.737.0
37.9
38.838.7
39.1
39.539.7
40.741.040.4
40.8
41.241.5
20.0
21.0
22.0
23.0
24.0
25.0
26.0
27.0
28.0
29.0
30.0
31.0
32.0
33.0
34.0
35.0
36.0
37.0
38.0
39.0
40.0
41.0
42.0
43.0
44.0
45.0
1940 1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020
Years
The forest coverage rate (%)
0.0
5.0
10.0
15.0
20.0
25.0
30.0
35.0
40.0
45.0
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
1985 1990 1995 2000 2005 2010 2015 2020
Years
Forest area (% of land area)
Vietnam
Laos
Malaysia
Cambodia
Thailand
China
Philipines
Indonesia
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If we measured by the forest restoration status (100 - the forest coverage rate),
the line is as U-shaped inverted of Kuznets. This shows that it was associated with
the economic development achievements for over time, the forest restoration status
has trends to correspond with the high level of economic development. At the Figure
7 showed that the relationship between the forest coverage rate and the Vietnam’s
economic development level are U-shaped and it went-up. However, we lack of data
before 1990, so the shape is not as completed as the U.
Fig. 7. The relationship between the forest coverage rate and GDP per capita
(1990 - 2017)
Source: Authors processed from sources of General Statistics Office and
some relation studies in Vietnam.
4.2. The impacts of protection policy - forest restoration
Since Law on Forest protection and development was issued (National
Assembly of Vietnam,1991), the forest area was increased due to zoning, to promote
natural regeneration and new planting in some years ago, that’s always higher than
the forest area before by legal or illegal exploitation. Policies of forest allocation
(Prime Minister, 2001), Ministry of Defence coordinated with local governments to
identify forest areas that are seriously deforested, especially in the central highlands,
southeast and north central regions for organizing military units stationed, locked,
built defense and security areas associated with forest protection, force layout,
permanent means for readying to take part in anti-deforestation (Ha Cong Tuan,
2009), forest area is increased in the sustainable trend.
25.0
27.0
29.0
31.0
33.0
35.0
37.0
39.0
41.0
43.0
500 1000 1500 2000 2500 3000
GDP/person (price of 2010, 10 thousand Vietnam Dong)
The forest coverage rate (%)
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On the basic practice of policy impacts in protecting and forest development,
the study built following hypothesis:
H0: There is no difference between the forest coverage rate (%) and the forest
restoration and protection policies’ impact.
H1: There is difference between the forest coverage rate (%) and the forest
restoration and protection policies’ impact.
Table 2: The definitions of the inspection model’s variables.
No. Variable symbols Contents Measurement
1 PI (Policy Impact) Policy impact Yes =1; No = 0
2 FC (Forest cover) Forest coverage rate %
In 1991, Law on forest protection and development was issued and some
guidelines, policies were also issued. Assumption study has policy impact from 1994.
Database from 1943 to 2017. According to Kendall and Stuart (1979), used t- test for
independent samples is suitable.
Table 3: The results of testing for independent samples.
Levene's Test
for Equality of
Variances
t-test for Equality of Means
F Sig. t df
Sig. (2-
tailed)
Difference
average
Difference
standard
errors
95% Confidence
Interval of the
Difference
Lower Upper
The
forest
coverage
rate (%)
Assuming
variance is
equal.
.048 .827 3.659 30 .001 6.365 1.739 2.812 9.917
Assuming
variance is
not equal.
3.277 12.025 .007 6.365 1.942 2.133 10.596
In the Table 3, the difference average ratio of the yearly forest coverage rate
has policy impacts and was not 6.365%, estimate the confidence level: 95% is [2.8%;
9.9%]. Levene testing was 0,827 > 0,05, t-testing with the total variance was 0.01 <
0.05. Assuming H1 was suitable. So, it affirmed the Government's policies impact
make sense to restore forests in Vietnam.
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4.3. Results of regression model
The results in the Table 4 showed that GP variable impacted to FC variable
did not statistically significant. The variables of YP, PR, YP square impacted to the
forest coverage rate with the confidence level was over 95%. The model was tested:
ANOVA, residual correlation, residual variance and R2 adjusted = 0.97 (97% change
of the forest coverage rate was explained by independent variables).
PR (Percentage of rural population, %) has an adverse impact to FC. When the
percentage of rural population is growth, the forest coverage rate will be decreased.
YP (GDP/person) has an adverse impact to FC. The more the YP’s big, the
more the forest coverage rate will be decreased.
YPS (YP square) has the same directional impact FC. The more the YP’s big,
the more the forest coverage rate will be increased (as the economic development
level is high).
Table 4: Regression coefficient
Unstandardized
coefficients
Standardized
coefficients
t Sig.
B
Standard
errors
Beta
(Constants) 99,556 27,952 3,562 0,002
PR (Percentage of rural population, %) -1,242 0,322 -1,155 -3,859 0,001
(GP) Growth population GDP (%) -0,938 1,280 -0,031 -0,733 0,471
YP (GDP/person) -1,128 0,182 -1,695 -6,204 0,000
YP square 17,193 1,981 1,482 8,680 0,000
Dependent variable: FC (Forest coverage rate, %)
ANOVA: Value F = 288,81; Sig. = 0,000.
R2: 0,97; Sig. = 0,000.
d (Durbin - Watson): 1,477
Spearman testing: All regression coefficients have Sig. > 0,05.
The result showed that the relationship between the forest restoration status
and the economic development is as the U-shaped or the relationship between the
forest degradation status and the economic development is as the U-shaped
invertation Kuznets.
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5. Policy implications
The study results affirmed three problems that we must to solve basing on the
relationship between the economic development and the forest restoration status, as
the following:
Firstly, to focus on maintaining economic growth and improve labor
productivity for upgrading the economic development level (GDP/person) will be the
core of maintaining forest restoration in Vietnam.
Secondly, to accelerate the process of industrialization and urbanization in
rural areas for decreasing the proportion of rural population will be the best method
to maintain the sustainable restoration of forests.
Thirdly, laws and the Government’s policies affected to the forest coverage
rate. The Government should be completed forest protection and restoration policies
in current conditions. Specially, attention to maintain the coordination with Ministry
of Defence and the local authorities in key provinces that it has a large forest area in
protection and afforestation.
Although the study is efforted to used database of 27 years, the data before
1990 is rare, especially the period of Vietnam’s forest was serious degraded, so the
study results are limited.
References
1. Alam M., Sathaye J., Barnes D. (1998). Urban household energy use in India:
efficiency and policy implications. Energy Policy 26 (11): 885-891.
2. Balat, M., & Ayar, G. (2005). Biomass energy in the world, use of biomass and
potential trends. Energy sources, 27(10), 931-940.
3. Barbier EB, Burgess JC, Grainger A (2010). The forest transition: Towards a
more comprehensive theoretical framework. Land Use Policy 27 (2): 98-107.
4. Belov, S.V. (1976). Forest pyrology (in Russian). Leningrad Forestry Academy
of the USSR, St. Petersburg.
5. Bhattarai M., & Hammig M. (2001). Institutions and the environmental Kuznets
curve for deforestation: a cross-country analysis for Latin America, Africa and
Asia. World Development 29 (6): 995-1010.
6. Culas, R. J. (2007). Deforestation and the environmental Kuznets curve: An
institutional perspective. Ecological Economics, 61(2-3), 429-437.
7. Davis M. (1998). Rural household energy consumption: The effects of access
to electricity-evidence from South Africa. Energy Policy 26 (3): 207-217.
1083
8. Ewers R.M. (2006). Interaction effects between economic development and
forest cover determine deforestation rates. Global Environmental Change 16
(2): 161-169.
9. Hà Công Tuấn (2009). Tổng quan về bảo vệ rừng Việt Nam và các giải pháp
bảo vệ rừng. Truy cập từ ,
tháng 9 năm 2017.
10. Jesús C.C, Olha D. Steffen F., Ian Mc. Michael O. Linda S. & Brian W. (2017).
Economic Development and Forest Cover: Evidence from Satellite Data.
Science Report 7: 40678.
11. Kendall, M. G., and Stuart, A. (1979). The Advanced Theory of Statistics. New
York: Macmillan.
12. Koop G., & Tole L. (1999). Is there an environmental Kuznets curve for
deforestation? Journal of Development Economics 58 (1): 231-244.
13. Kuznets, S. (1955). Economic growth and income inequality. The American
Economic Review 45 (1): 1-28.
14. Lambin EF., & Meyfroidt, P. (2010). Land use transitions: Socio-ecological
feedback versus socio- economic change. Land Use Policy 27 (2): 108-118.
15. Laurance WF. (2007). Forest destruction in tropical Asia. Current Science 93
(11): 1544-1550.
16. Leach MC. (1992). The energy transitions. Energy Policy 20 (2): 116-123.
17. Mather A.S. (2007). Recent Asian forest transitions in relation to forest-
transition theory. International Forestry Review 9 (1): 491-502.
18. Miah M.D, Masum M.F.H, Koike M, Akther S. (2011). A review of the
environmental Kuznets curve hypothesis for deforestation policy in
Bangladesh. iForest 4: 16-24.
19. Quốc hội (1991). Luật bảo vệ và phát triển rừng. Truy cập từ
, ngày 17 tháng 10 năm 2018.
20. Rudel T.K., Coomes O.T., Moran E., Achard F., Angelsen A., Xu J., Lambin E.
(2005). Forest transitions: towards a global understanding of land use change.
Global Environmental Change 15 (1): 23-31
21. Scrieciu SS. (2007). Can economic causes of tropical deforestation be identified
at a global level? Ecological Economics 62: 603-612.
22. Shafik, N., & Bandyopadhyay, S. (1992). Economic growth and environmental
quality: time-series and cross-country evidence (Vol. 904). World Bank
Publications.
23. Tổng cục Thống Kê (1990–2018). Dữ liệu thống kê. Truy cập từ
, tháng 9 năm 2018.
1084
24. Tổng cục Thống Kê (1990–2018). Báo cáo tình hình kinh tế- xã hội (các tháng,
quí, 6 tháng, năm). Truy cập từ
https://www.gso.gov.vn/default.aspx?tabid=717, tháng 9 năm 2018.
25. Thủ tướng (2001). Quyết định về quyền hưởng lợi, nghĩa vụ của hộ gia đình, cá
nhân được giao, được thuê, nhận khoán rừng và đất lâm nghiệp, ngày 12 tháng 11
năm 2001. Truy cập từ < https://thuvienphapluat.vn/van-ban/Lao-dong-Tien-
luong/Quyet-dinh-178-2001-QD-TTg-quyen-huong-loi-nghia-vu-cua-ho-gia-
dinh-ca-nhan-duoc-giao-thue-nhan-khoan-rung>, ngày 17 tháng 10 năm 2018.
26. Winslow M. (2005). The environmental Kuznets curve revisited once again.
Forum for Social Economics 35 (1): 1-18.
27. WB (2018). World Development Indicators: Forest area (% of land area).
.
28. Yandle, B., Vijayaraghavan, M., & Bhattarai, M. (2002). The environmental
Kuznets curves. A Primer, PERC Research Study, 02-01.
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