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MINISTRY OF EDUCATION
AND TRAINING
VIETNAM ACADEMY OF SCIENCE
AND TECHNOLOGY
GRADUATE UNIVERSITY OF SCIENCE -----------------------------
DOAN THI TRUONG NHUNG
RESEARCH OF LANDSCAPE ECOLOGY IN SON LA PROVINCE
TO SERVE SOCIO-ECONOMIC PLANNING AND DEVELOPMENT
Major: Ecology
Code: 9 42 01 20
SUMMARY OF BIOLOGY DOCTORAL THESIS
Hà Nội - 2018
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This thesis was finished at:
Graduate University of Science and Technology – Vietnam Academy of Science and
Technology
Supervisor 1: Asc. Prof. DSc. Tran Dinh Ly
Supervisor 2: Dr. Ha Quy Quynh
Reviewer 1: ……………………………………………………………….
Reviewer 2: ……………………………………………………………….
Reviewer 3: ………………………………………………………………..
The theisis will be defended in Committee in front of the thesis assement
committee at Graduate University of Science and Technology – Vietnam Academy
of Science and Technology
at ….hour….. on …………date …..….month…….year 2018
The thesis shall be found at:
- The Library of Vietnam Academy of Science and Technology
- The Vietnam National Library
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INTRODUCTION
1. The significance of study
Son La province locates in the North West of Vietnam, which is essential
geological position in socio-economic development strategy and protection of
national and regional security and defense. Moreover, Son La is ensuring national
and regional security and defense. Simultaneously, having the watersheds of Da and
Ma River, this province is the crucial protection area for the Northern Delta and has
the two largest hydropower projects in Vietnam. With the terrain predominated by
low mountain, highlands and valleys, abundance of land and climate resources, and a
special local knowledge system, Son La has great prospects for developing
agriculture, forestry, trade and tourism, bringing socio-economic and environmental
efficiencies.
However, low effectiveness of natural resource protection in Son La has
positive effects on other regions in the downstream of Da River and Ma River. In
recent 10 years, land use system and in structure of cultivated plants have been
change rapidly. In the province, land degradation has been more seriously, water
resource has been degraded; environment pollution caused by deforestation and
agricultural chemical and natural hazards have been more frequently and caused more
and more risks [84]. Thus, in long term strategy of socio-economic development need
scientifically consider rapid and sustainable development following functional
regions.
Researching landscape ecology (LE) is a synthetic and interdisciplinary approach
from research of species structure, environment characteristics, ecological and
regional conditions, and distributional regions. Researching ecological landscape
aims to clearly understanding of natural resources and natural conditions; the
interaction relation among natural components; features and functions of each
territorial unit, etc. which are foundations of new proposals of properly and
sustainable natural resource extractions and uses.Thus, nowadays, it is necessary to
research ecological landscapes in Son La province aiming to orientation of ecological
function exploitation, reformation and rehabilitation of provincial territory.
In this fact, the study of "Research of landscape ecology in Son La provinces to
serverve socioeconomic planning and development" contributes to sustainable socio-
economic development in Son La province.
2. Thesis Ojectives
The thesis aims to:
- Classify landscape ecology system and establish maps of landscape ecology in
Son La province
- Clarify the changes of landscape ecology in Son La over time (from 2005 to
2015)
- Identify the scientific foundations based on studing landscape ecology to
orientate rational territory use in agriculture, forestry and conservation
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3. Main contents of the thesis
- Scientific bases of LE and classification of LE
- Characteristics of components of the LE in Son La province such as natural
features, socio-economic characteristics, humans and human activities
- System of landscape ecology in Son La province
- Assessment of the changes of the landscape ecology system in Son La
province.
- To propose solutions for rational and sustainable use of natural resources in Son
La province.
CHAPTER 1. LITERATURE REVIEW AND SCIENTIFC BASES OF STUDY
ISSUES
1.1. Scientific fields related to landscape ecology
1.1.1. Ecology
Ecology originated from Greek, “Oikos” means "house" or "living relation";
“Logos” means "study of". Thus, ecology means the scientific study of the relations
of organisms and their habitats. There are many different definitions of ecology, but,
generally, they are united that: ecology is a biology science that studies the
interrelations between organisms and the environment.
1.1.2. Ecosystem
Ecosystem concept: Vu Trung Tang (2003) [63] defined: “ecosystem is a
combination of biomes with their physical environment where they are existed, in
which, organism interact each other and with environment to create a material cycle
and energy metabolism"
Ecosystem components: Ecosystem includes two basic components: biomes và
physical environment.
Ecosystem structure: Including biomes, their physical environment,
interrelations among organisms, interactions between organisms and their
environment.
Ecosystem functions: The basic function of the ecosystem is the
implementation of the material cycle, energy and information exchange to recombine
biomes adapting with condition of biophysical environments, creating a dynamic
balance in development process.
Ecosystem Nature: Ecosystem has some features, three most significant
features of which have been mentioned in this part, including:
- Ecosystem is a constantly moving and changing system, the static state is
only relative and temporary.
- Ecosystem is an adjustable dynamic balance system
- The higher the diversity, the greater the sustainability
1.1.3. Landscape study
Concept of landscape
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In this thesis, LE is defined as a form concept. "landscape is a complete part of the
earth's surface with geomorphology, structure, and determined complexion in the
development process and causal relations of impact factor integration" [97].
Elements of landscape forming
In Son La province, the thesis analysed the culture features, the role of landscape
forming factors and the relationship between them, and at the same time, grouped
these elements. Group of abiotic elements includes: geological background, terrain
and processes of geomorphology, climate and hydrology. Group of biotic elements
includes soil, biological system, duration and human activities.
System of landscape classification
Pham Hoang Hai and his colleagues (1997) constructed a landscape classification
system applied to the Vietnam territory at the map of a 1/1,000,000 scale with 7
levels: Landscape systems →Landscape subsystems → Landscape class →
Landscape subclass → Landscape type → Landscape sub-type → Landscapes kind
[27].
Structure and dynamic of landscapes
- Landscape structures include horizontal, vertical and temporal structure
- Landscape dynamic and changes
Landscape functions
Landscape functions have different conceptions
1.1.4. Biogeocenology
Biogeocenos are defined as "synthesizing natural phenomena on a certain surface in a
accordant manner with the matter exchange and transformation flow among natural
conditions (mother rocks, floras, faunas, micro-organisms, soils and hydro-climatic
conditions), which have particular characteristics for the interactions of the
constituent elements and have the specific types of material and energy exchanges
between them and other natural phenomena and is a dialectical unity having initial
contradictory in the constantly movement "(Sukachev, 1947) [122]. In a simple
understanding, biogeocenos includes biocoenosis and habitat. The nature of the
interrelationship between the components of biogeocenos is the processes of matter
and energy accumulation and transformation (Sukachev called the process of
biogeocenos) that decide the arising, growth, development and ecological succession
of forest ecosystems.
1.2. Research review of Landscape Ecology
1.2.1. Concept of landscape ecology
Definitions of landscape ecology focusing on ecological specialties of
landscape
The most common point of definition focuses on two important aspects of
interaction between organism and its environment that enables to differentiate
between landscape ecology research and ecology research.
Definitions focus on humanity features of landscapes
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In this way, the definitions focus on the theoretical points that this is general
and interdisciplinary sciences that study the relationship between human and the
landscape.
Landscape ecology of landscape scientists in Soviet and Vietnam
According to Soviet landscapeologists, LE is a new discipline of landscape
study, in which, humans are included as a part of the landscape in the form of
economic activities and surrounding elements forming the landscape [72].
In Vietnam, all the most important definitions of the LE are given by
geographers. LE is a discipline of applied landscape study, with particular emphasis
on ecological features of geology. Subjects of LE study are specific units with their
own principles, methods, and special regulation to classify them in the spatial
dimensions [27].
Integrated definition of landscape ecology
LE has two basic aspects: teritorial landscape and ecosystem of lanscape.
These two aspects are independent but link closely together in a united territory. The
LE theory issues are also the unification of landscape theory and the ecosystem
theory. Thus, the LE is a science studying and explaining the interactions of the
system of biotic and abiotic elements in the definite space of the landscape.
Studying landscape considers two directions including landscape compositions
and entire of landscape, while studying LE focuses on the ecological characteristics
of landscape components. Each landscape component is specifically considered in
terms of environment of the organism, and interacting with the organism according to
ecological laws [72]
1.2.2. Structure and functions of landscape ecology
The structure of LE consists of the landscape structure (the natural geographic
components of the landscape) and the ecosystem structure (organic and inorganic
materials, producers, consummers and decomposers) which are intergrated in a unity.
The function of LE is multifunctional, including the natural functions of the
landscape and the ecological functions of the ecosystem. The change of any structural
element of the landscape will cause the change of other components and the change of
landscape and all landscape functions.
1.2.3. Differentiation between “Landscape ecology” and “Ecological Landscape”
“Landscape ecology”: is the intermediate science between ecology and
landscape where ecological content is more focused than ecological issues in the
landscape, the centre of reflection is the ecosystems within the landscape boundary
[87].
“Ecological landscape”: In the foreign references, we only found the term of
Landscape Ecology (or Landschafts Oekologie in German) while the term of
Ecological Landscape (Oekologische Landschaft) has not been found.
The explanation for the two concepts presented by Nguyen The Thon (1993)
[74] differentiated unclearly these two concepts. Therefore, this research
recommends using the term of Landscape Ecology only.
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1.2.4. Literature review of Landscape Ecology
On the world
Ecologycal study of landscape has begun in the second half of the 1960s at the
Institute of Biology Landscape at the Academy Sciences of Czechoslovakia (1967).
The Fifth Conference (1974) initiated the establishment of the International
Association of Landscape Ecology (IALE), the first of meeting was held in Denmark
in 1984. It i scan be seen that ecologycal study of landscape means determination of
ecological characteristics and norms of a landscape in order to protect and improve
the environment [72].
In Vietnam
The study contents of the landscape ecology have become clearly since Vietnam
joined the International Association of Landscape Ecology in 1992. Researches in
this period is oriented and had research scale in accordance with demands for
economic development and environmental protection at the territorial level. Most of
the landscape ecology studies in Vietnam have been conducted following the
landscape structure analysis, landscape assessment, and determination of ecological
economic models.
1.3. Studies related to thesis topic in Son La province
Many previous studies related to the thesis topics, in different fields, are carried
out in different periods. The authors investigated on the natural, socio-economic
conditions of Son La province and grouped of researches implemented in the territory
of Son La province.
1.4. Theoretical bases
Based on scientific publications of ecosystem, landscapes, this thesis create
foundation theory for studing LE in Son La. The scientific contents and theory for
thesis approaching the research isues include:
- The term of „landscape ecology“ or „ecology study of landscape“ has the same
definition of natural objects, thus, the thesis uses the term of „landscape ecology“.
- The viewpoint:"LE is the science of studying the interactions between
organisms and the environment, organisms and organisms in a certain area limited by
the landscape" (Schubert, 1986, p. 447) [121] was used in this study. LE units are
ecosystems
- LE has clear hierarchy and classification as follows: LE system – LE sub-
system - LE class – LE sub-class - LE type – LE sub-type – LE kind. The objects of
LE study is the ecosystem in the landscape. Therefore, the specific object in this
thesis is sub-system of monsoon tropical monsoons LE with mild winters and a dry
season in Son La.
Because the separate classification for LE in Son La province has been
inexistent, the thesis used the landscape classification by Pham Hoang Hai et al.
(1997) [27] as a foundation for ranking the levels of the LE system in Son La
province. From the theoretical and scientific bases, the criteria for applying LE
classification, the thesis gave the classification criteria for the research area following
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the hierarchy of system sub-system class sub-class sub-class type
sub-type kind.
CHAPTER 2. RESEARCH CONTENTS, VIEWPOINTS AND METHODS
2.1. Research Contents
- Scientific bases of landscape ecology and landscape ecology classification
- Characteristics of components of landscape ecology in Son La: Natural - social -
economic conditions - human beings and human activities
- System of landscape ecology in Son La
- Change assessment of landscape ecology system in Son La
- Suggestion of solutions for sustainable and proper use of natural resources in
Son La
2.2. Theoretical viewpoints of the research
2.2.1. Systematic viewpoint
The basis of the systemic viewpoints is the conception of the unity and
completeness of internal relationships and the distribution of the external linkage of
the system.
2.2.2. Synthetic viewpoint
Synthesis is considered at two different views: (1) Synthesis is the process of
comprehensive research on the natural and socio-economic conditions, the
relationships between organisms in the ecosystem in the territory of the landscape. (2)
Synthesis is a systematic and regulative combination based on comphrehensive and
integrated analysis of the elements and factors of natural terrestrial aggregates,
simultaneously, identifies biological laws, relationships between organisms in the
geographic locations
2.2.3. Territorial viewpoint
For the evaluation process to be effective, research should establish theoretical
and practical issues related to organization and planning based on the approach of the
territorial point of view. This ensures that the research territory is assessed not only in
relation to neighbouring territories, but also for the specific characteristics of Son La
province.
2.2.4. Historical perspective
Every territorial unit or geographic entity has to go through the processes of
formation, development and evolution over time. Thus, the process of assessing and
perceiving the territory from a historical perspective is a full access to all aspects of
territory in the past and forecast of their changes in the future.
2.2.5. Interdisciplinary and sustainable development viewpoints
Sustainable Development (SD), a new and comprehensive aspect, has great
concerned when the economic development affects on the human environment and
natural resources. Research and assessment of landscape ecology from the SD point
of view is understood to be an evaluation for each unit level based on an integrated
assessment of the constituent elements, structure and functions of the landscape
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ecology. Using landscape ecology units ensures economic, environmental and social
factors in practice application.
2.3. Research methods
2.3.1. Fieldworks
The fieldworks were conducted based on a detailed survey of the formation factors
and the landscape slice.
Main survey routes and timeframes include:
- Route 1: Son La - Bac Yen - Phu Yen: April 15th - 14th, 2014.
- Route 2: Son La - Thuan Chau - Muong La - Quynh Nhai: May 20 to 27, 2015.
- Route 3: Son La - Mai Son - Yen Chau - Moc Chau: from March 1 to March 8,
2016.
2.3.2. Data and document analysis and synthesis
Materials, data related to research topic, research areas are collected, selected,
processed and systematized.
2.3.3. Mapping and GIS
Map is considered as the second language of geography, because they are the most
visible expressing spatial features of the research objects. Digital maps have enough
spatial and attribute information for the features of interest, helping the composite
mapping process to be performed accurately and objectively. Mapping and
geographic information systems (GIS) are used in a various context throughout the
research process.
2.3.4. Professional expert interview
The researcher has consulted experts and scientists from the Institute of Ecology and
Biological Resources, Institute of Geography, Vietnam Academy of Science and
Technology, Department of Agriculture and Rural Development, Department of
Natural Resources and Environment, Department of Science and Technology of Son
La province; Son La Forest Protection Department, Son La Nature Reserve
Management Board, University of Natural Sciences - VNU, Tay Bac University ...
2.3.5. Method group of landscape ecology research and assessment
The methodology group includes:
- Method of Conjugate component map analysis
- Method of the dominant factor analysis
- Method of LE mapping
- Method of landscape zoning
2.4. Steps of research
The research was done by this following main steps:
Step 1. Difined the ojectives, duties and scales and contents of research
Step 2. Collecting and reviewing typical issues related to thesis topic, at the
same time, doing the field trips and identifying the differented characteristics of the
constituent factors and their role in LE of Son La province.
Step 3. Research the landscape and LE classification systems, then, construct
the 1:100.000 scale map of LE in Son La.
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Step 4. Calculate the area of each LE kind over time and the changes of each
LE kind.
Step 5. Give orientation of proper exploitation and use of territory toward
socio-economic developmemt.
CHAPTER 3. RESULTS AND DISCUSSION
3.1. Natural conditions, human ecology elements - formation factors of landscape
ecology
3.1.1. Natural conditions
Geographical location
Son La is a mountainous province in northwestern Vietnam, far 280 km from
south-east of Hanoi, with a total natural land area of 14,125 km², located in two large
basins of Da River and Ma River.
Located deeply in the continent, Son La is situated within the latitude of 20°39’
N to 22°02’ N and longitude of 103
°11’ E to 105
°02’ east longitude. It borders with
Yen Bai, Lao Cai provinces to the north, with Phu Tho, Hoa Binh province to the
east, with Lai Chau, Dien Bien provinces to the West and Thanh Hoa province, Laos
to the south
Geology - Typography
Geology: Son La belongs to the geosyncline zone of Da River, located between
the two tectonic complexes of Hoang Lien Son mountain range and Ma River with
deep-marine sediments of limestone, metamorphic schist and basis and acidic magma
intrusive blocks.
Typography: The arrangement of mountain ranges, terrain types and tropical
monsoon regimes divide Son La into different natural areas such as: upland, midland
and lowland with specific characteristics of climate. The largest limestone range in
the north goes through Son La in the northwest - southeast direction, intercalated by
the sediment of clay forming the system of Son La - Moc Chau plateau. This is a
terrain type with special features of the province.
Climate and Hydrology
Climate: Son La has a humid tropical monsoon climate, with mild winters and
a dry season. Climate has a strong impact on the physical, chemical and biological
processes of soil and rock.
Hydrology: Territorial topography features create a dense network of rivers and
streams in Son La that flow into the Da and Ma rivers. Therefore, these two rivers are
the main hydrological systems of Son La and the natural boundary of the huge
waterway of the Xu Xen Chao Chai Range.
Soil
Results of soil survey, editing, land mapping at the rate of 1:100,000
(according to the soil classification system 1976-1984) in 2004 of the National
Institute of Agricultural Planning and Projection shown that land resources in Son La
province contain 7 groups with 24 types (mapping unit) with 1,329,644.1 ha,
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accounting for 94.61% of the total natural area of the province (Table 3.1),
(Figure 3.4).
Floras
Because of characteristics of geographical location, topography, climate and soil, Son
La province has very different ecosystems, the floras of conservation areas, special-
use forests, production forests and cultivated areas are also different from those in the
North East, the Red River Delta and elsewhere. Over time, the area of natural forests,
plantation forests have been evolved according to the demands of each period for war
serves, economic construction and people's life. In general, the natural forests in Son
La province have been degraded considerably, the areas of bare land and hills have
been increased. Despite the investment of the province to restore the forest, create a
material source to meet the essential needs, both positive and negative human impacts
have changed the appearance of forests in Son La.
Natural forests have retreated to areas with difficult terrain, few inhabitants, or only
protected in nature reserves, instead of regenerating forests, plantation forests,
industrial plants with industrial trees, fruit trees and up-land fields. Reforestation,
zoning for protection and rehabilitation have great efforts, however, a large area of
bare hills widely still distributes in all topographic types and forms.
The vegetation cover in Son La province is classified into four classes according to
the classification framework of UNESCO 1973 (Figure 3.5).
Class I: Closed forests are determined by over 60% of the wood tree covers and from
5m height of the trees
Class II: thin forests are defined by the canopy cover (k) from 0.3 to 0.6. Some
authors argued that this type of forests exists in some small areas in Moc Chau,
Thuan Chau and Yen Chau districts (Son La). Through the survey, this forest types in
Son La was almost depleted or cut down and to be shrub or grass cover
Class III: Shrubs include woody vegetation cover with a height of 0.5 - 5m,
possibly with scattered wood trees with canopy cover under 0.3. This class mostly
have secondary origin and was regenerated after clear cutting or slash and burn. Only
bushes on high mountains are primeval nature.
Class IV: Grassland
Most of the grasslands in Son La have secondary origin and are formed after
clear cutting or slash and burn to create large gaps for grass growing
3.1.2. Elements of human ecology
Ethnics and Population:
There are 12 ethnic groups in Son Lan, in which, the Thai have the most
population, following by the Kinh, the H'mong, the Muong, the Dao, the Khơ Mú and
others (Kháng, La Ha, Lào, Hoa, Xinh Mun...).
Poverty reduction and employment:
In recent years, the National Program on Hunger Eradication and Poverty
Reduction, socio-economic development projects such as Program 135; 134; sedentary
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farming program; rural clean water and sanitation, etc. along with policies such as
policy 120; subsidy policy, … have been done in Son La
Economic structure:
The economic growth rate in 2014 was higher than that of 2013 (10.26% in
2013 and 11.28% in 2014). The economic structure continued to change positively:
the service sector increased from 40.92% in 2013 to 42.3% in 2014, occupied high
proportion and are the most contribution of the economy; the industry-construction
sector grew from 24.92% in 2013 to 26.65% in 2014; the agriculture, forestry and
fishery sector decreased from 34.16% in 2013 to 31.05% in 2014.
Human impacts on the natural environment
Water Environment: Surface water and groundwater in Son La province are
polluted mainly by agricultural activities, urban and industrial wastewater, loss of
upstream forests, migration and resettlement.
Air environment: Human activities that polluted the air environment include
construction, transportation, industrial production, forest fire and mining.
Soil environment: The soil environment in Son La province is polluted and
degraded due to migration, resettlement, agricultural production, industrial
production, natural disasters and environmental incidents.
3.2. Classification system of landscape ecology in Son La province
Based on analyzing the components of the landscape ecology system in Son La
province, we set up the system of classifying the landscape ecologies in Son La
province as follows: Son La is in the monsoon tropical zone, has a cold winter and a
dry season. Thus landscape ecology is formed 4 classes, 5 sub-classes, 13 types, 33
sub- types and 63 kinds (table 3.2)
Table 3.2. Statistics of landscape ecology units in Son La province System/
sub-systems
Class Sub-class
Type Sub-type Area (ha)
LE system
of moonso
on tropical, LE sub-type of moonso
on tropical with a mild cold
winter and a
Mountain LE class (SLI)
High mountai
n LE sub-class
(SLI-1)
1. Evergreen temperate and sub-tropical forests on high mountains, total of annual temperature under 5.500ºC, average annual temperature <10ºC, amount of rain: moderate to high, cold season has at least 8 months, dry season from 3-4 month, and a drought month (SLI-1-k1)
1. Forests on Humic Chromic Luvisol, including LE kind of 1a, 1b
2,172.56
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System/ sub-
systems Class
Sub-class
Type Sub-type Area (ha)
dry season
2. Temperate and sub-tropical evergreen shrub on high mountain, annual temperature total: under 5.500ºC, annual average temperature: under 10ºC, cold season:8 months (SLI-1-k2)
2. Evergreen shrub on Humic Alisols including kind of 2g
35.21
LE sub-calss of everage mountai
n (SLI-2)
3. Evergreen temperate on everage mountain forest, total of annual temperature under 5500°C, annual average temperature of 10 - 15°C, moderate rainfall, cold season in over 8 months, dry season in 5 - 6 months, in which 0÷3-month drought (SLI-2-k1)
3. Closed evergreen closed forests on Humic Alisols, including LE kind of 3c
745.90
4. Forests on Humic Ferrasols including LE kind of 4c
21,925.52
4. Sub-tropical bushes and grasses. Total of annual temperature under <5.500°C, average temperature from 10°C to 15° C, moderate rain. Cold season is less than 8 months, dry season is 5-6 months. The major botanical components are sub-tropical taxa. (SLI-2-k2)
5. Shrubs and grasses on Humic Ferralsols, incl. kind of 5g.
1,189.71
6. Shrubs and grasses on Orthic Ferralsols, incl. kind of 6g
852.37
LE sub-class of
low
5. Closed evergreen sub-tropical forests The total
7. Forests on Chromic Ferrasols, incl. kind of 7c
172,591.01
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System/ sub-
systems Class
Sub-class
Type Sub-type Area (ha)
mountains
(SLI-3)
temperature of 5.500° - 7.300°C, the average temperature is 15 - 20°C, heavy rain, 4÷7-month seasons, 3÷4 month dry seasons, 0÷1-month drought (SLI-3-k1)
8. Closed evergreen sub-tropical forests on Orthic Ferralsols, incl. kind of 8c
96,940.17
9. Closed evergreen sub-tropical forests on Ferralic Acrisols, incl. kinds of 9c, 9e, 9f, 9k
63,845.74
10. Closed evergreen rainforests on Ferralsols, incl. kind of 10c
18,553.47
11. Mix bamboo forests on Ferralsols, incl. kind of 11e
5,341.79
6. Closed deciduous and semi-deciduous tropical rainforest (SLI-3-k2)
12. Closed deciduous and semi-deciduous tropical rainforests on Orthic Ferrasols, incl. kind of 12d
4,376.52
7. Tropical bushes and grasses (SLI-3-k3)
13. Tropical bushes and grasses on Orthic Ferralsols incl. kinds of 13g, 13i, 13k
43,383.45
14. Shrubs and bushes on Ferralic Acrisols, incl. kinds of 14g, 14i, 14k
103,482.64
15. Shrubs and bushes on other Ferrasols, incl. kinds of 15i, 15k
78,271.41
16. Shrubs and bushes onn Dystric Gleysols, incl. kind of 16i, 16k
3,620.75
17. Bushes on Chromic Ferralsols, incl. kinds of 17g, 17i, 17k
32,556.56
LE class of Pleatau
LE subclass of Son
8. Closed evergreen tropical rainforests, on the altitude of
18. Closed evergreen tropical rainforests Chromic Ferralsols,
37,314.74
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System/ sub-
systems Class
Sub-class
Type Sub-type Area (ha)
(SLII) La pleatau
500 - 900m (1000m). Total of annual temperature over 7,300°C. Annual rainfalls from 500 - 2500 mm. <4 cold months. Everage temperature >20 ° C, 3÷4-month dry season, 0÷1-month drought. Major botanical components are tropical taxa (SLII-k1)
incl. kinds of 18c, 18e, 18f
19. Closed evergreen tropical rainforests on Ferrasols, incl. kinds of 19c, 19f
32,720.81
20. Closed deciduous and semi-deciduous tropical rainforests on Chromic Ferralsols, incl. kind of 20f
917.49
21. Closed deciduous and semi-deciduous tropical rainforests on Acric Ferralsols, incl. kind of 21i
57,103.79
10. Tropical Shrubs and grasses (SLII-k3)
22. Shrubs and grasses on Chromic Ferralsols, incl. kinds of 22g, 22i, 22k
125,837.86
LE class of
hills and
lowlands at the altitude under 500m
(SLIII)
11. Closed evergreeen tropical rainforests Total of annual temperature over 7300°C, average annual temperature >20°C, annual rainfalls are 1500- 2500 mm, <4-month cold season, 3÷4-month dry season, 0÷1-month drought, major botanical
23. Closed evergreeen tropical rainforests on Orthic Ferralsols, incl. kind of 23e
5,539.85
24. Closed evergreeen tropical rainforests on Chromic Ferralsols, incl. kinds of 24c, 24e, 24f, 24k
133,088.76
25. Closed deciduous
and semi-deciduous tropical rainforests on
12,697.82
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System/ sub-
systems Class
Sub-class
Type Sub-type Area (ha)
components are tropical taxa (SLIII-K1)
other Ferrasols, incl. kinds of 25c, 25e 26. Closed deciduous and semi-deciduous tropical rainforests Ferralic Acrisols, incl. kind of 26e
1,943.37
12. Closed evergreen tropical rainforests Total of annual temperature >7300°C; evarage annual temperature > 20°C, annual rainfalls are 1500 - 2500 mm, <4-month cold season, 3÷4 -month dry season; 0÷1-month drought; major botanical components are tropical taxa, some of them migrate from the easth (SLIII-k2)
27. Closed deciduous and semi-deciduous tropical rainforests on Ferralic Acrisols, incl. kinds of 27c, 27e
25,541.54
28. Closed deciduous and semi-deciduous tropical rainforests on Chromic Ferralsols, incl. kind of 28d
263.07
29. Tropical shrubs and grasses on other Ferralsols, incl. kinds of 29g, 29i, 29k
87,688.30
13. Tropical shrubs and grasses (SLIII-k3)
30. Tropical shrubs and grasses on Chromic Ferralsol, incl. kind of 30i
3,263.44
31. Tropical shrubs and grasses on other Ferralsols, incl. kinds of 31i, 31k
187,967.04
32. Shrubs and grasses on Acric Ferralsols, incl. kinds of 32g, 32i, 32k
24,144.93
33. Bushes and grasses on Aluvisols, incl. kind of 33i
1,041.84
Rivers, streams, ponds,
Rivers, streams, ponds,
25,490.64
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System/ sub-
systems Class
Sub-class
Type Sub-type Area (ha)
lakes (SLIV)
lakes
Total 1,412,500.00
3.3. Change of Landscape ecology in Son La province
Based on the results of the formulation factor study of LE (terrain, soil,
climate) and hydrography, especially, the results of the vegetation cover survey in
2015 and documents collected from 2005, the thesis has established the map of LE in
2 periods of the year 2005 and 2015, and then assessed the variation of all types of
LE in Son La province.
3.3.1. Map of landscape ecology in 2005
Based on LE analysis, synthesis and mapping in Son La province in 2005
(Figure 3.16), then determined the area and position of each LE type, the area of LE
kinds in Son La province in 2005 is illustrated in Table 3.5 and figure 3.17.
Figure 3.17. The area of LE kinds in Son La province in 2005
At the year 2005, the major LE kinds in Son La were 7c, 24c with an area of
approximately 225,515.33 ha and 154,397.95 ha, respectively, followed by kind of
31i with an area of 149,101.44 ha and kinds of 22i with an area of 126,196.90 ha.
Some LE kinds have smaller area such as 8c, 18c and 9c with a total of area is about
240,029.69 ha. The smallest kinds are scrubs on humic Alisols (2g) with 35.24 ha;
residential land on low mountain (13k) with 59.79 ha; broadleaved deciduous and
semi-deciduous forests on Ferralsols (27d) with 51.22 ha; residential land in class of
hills and lowland (32k) with 63.16 ha; mixed broadleaved-coniferous forests on
Humic Chromic Luvisol (1b) with an area of 269.25 ha.
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3.3.2. Map of landscape ecology in 2015
By analyzing, synthesizing, mapping the STCQ of Son La province in 2015
(Figure 3.18), then determine the area and position of each type of STCQ. The area of
STCQs in Son La province in 2015 is shown in Table 3.5 and figure 3.19.
0
20000
40000
60000
80000
100000
120000
140000
160000
180000
200000
1a 3c 6g 9c 9k 12d 13k 14k 15k 17g 18c 19c 21i 22k 24e 25c 27c 29g 30i 32g 33i
Diện tích (ha)
Loại cảnh quan
Diện tích (ha)
Các loại sinh thái cảnh quan
Figure 3.19. The area of LE kinds in Son La province in 2015
In 2015, the major LE kinds are 7c with an area of 172,591.01 ha, 31i with an
area of approximately 155,293.45 ha, 24c with an area of 128,613,93 ha and 22i with
an area of 104,795.24 ha. Some smaller LE kinds are 8c, 9c and 14g with a total area
of about 211,110.95 ha. The smallest area of LE kinds are grasses and bushes on
humic Alisols (2g) with 35.21 ha; broadleaved deciduous and semi-deciduous forests
on Chromic Ferralsols (28d) with an area of 263.07 ha; mixed broadleaved-
coniferous forests on Humic Chromic Luvisols (1b) with an area of 268.98 ha.
3.3.3. Changes of landscape ecology in Son La over periods
Based on data of area of LE kinds in 2005 and 2015, the changes of area of LE
kinds between 2005-2015 are shown in Table 3.5 and figure 3.20.
Table 3.5. Changes of ara of landscape ecology kinds between 2005 and 2015
Unit: ha
No. Code of LE
kinds
Area of LE kinds
in 2005
Area of LE kinds
in 2015
Changes
between 2005 - 2015
1 1a 1,905.50 1,903.58 -1.92
2 1b 269.25 268.98 -0.27
3 2g 35.24 35.21 -0.03
4 3c 746.66 745.90 -0.76
5 4c 22,330.56 21,925.52 -405.04
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No. Code of LE
kinds
Area of LE kinds
in 2005
Area of LE kinds
in 2015
Changes
between 2005 - 2015
6 5g 1,190.91 1,189.71 -1.20
7 6g 853.23 852.37 -0.86
8 7c 225,515.33 172,591.01 -52,924.32
9 8c 102,901.40 96,940.17 -5,961.23
10 9c 65,702.57 59,107.08 -6,595.49
11 9e 133.76 133.62 -0.14
12 9f 3,749.50 1,912.24 -1,837.26
13 9k - 2,692.80 2,692.80
14 10c 21,641.40 18,553.47 -3,087.93
15 11e 5,567.10 5,341.79 -225.31
16 12d 4,380.95 4.376,52 -4.43
17 13g 5,530.24 8,747.37 3,217.13
18 13i 22,196.71 33,437.08 11,240.37
19 13k 59.79 1,199.00 1,139.21
20 14g 33,609.97 55,063.70 21,453.73
21 14i 26,212.11 45,738.75 19,526.64
22 14k 912.05 2,680.19 1,768.14
23 15g 21,175.06 21,959.09 784.03
24 15i 59,685.44 50,666.54 -9,018.90
25 15k 6,163.54 5,645.78 -517.76
26 16i 2,649.09 2,646.42 -2.67
27 16k 372.54 974.33 601.79
28 17g 8,645.78 8,629.80 -15.98
29 17i 20,175.52 17,160.58 -3,014.94
30 17k 2,927.74 6,766.18 3,838.44
31 18c 71,425.72 33,455.82 -37,969.90
32 18e 2,470.05 547.39 -1,922.66
33 18f 1,972.82 3,311.53 1,338.71
34 19c 21,082.33 29,477.79 8,395.46
35 19f 2,121.67 3,243.02 1,121.35
36 20f 918.41 917.49 -0.92
37 21i 1,241.73 57,103.79 55,862.06
38 22g 17,012.97 16,593.36 -419.61
39 22i 126,196.90 104,795.24 -21,401.66
40 22k 4,827.12 4,449.23 -377.89
41 23e 5,407.59 5,539.85 132.26
42 24c 154,397.95 128,613.93 -25,784.02
43 24e 962.80 964.66 1.86
44 24f 1,835.76 2,945.67 1,109.91
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No. Code of LE
kinds
Area of LE kinds
in 2005
Area of LE kinds
in 2015
Changes
between 2005 - 2015
45 24k - 564.50 564.50
46 25c 10,249.44 9,232.27 -1,017.17
47 25e 3,800.54 3,465.55 -334.99
48 26e 2,202.95 1,943.37 -259.58
49 27c 31,299.49 23,925.28 -7,374.21
50 27d 51.22 0 -51.22
51 27e 1.752.85 1,616.26 -136.59
52 28d 212.11 263.07 50.96
53 29g 52,418.83 50,964.86 -1,453.97
54 29i 20,616.71 20,724.18 107.47
55 29k 3,131.90 15,999.26 12,867.36
56 30i 1,723.80 3,263.44 1,539.64
57 31i 149,101.44 155,293.45 6,192.01
58 31k 22,775.38 32,673.59 9,898.21
59 32g 17,452.49 22,320.89 4,868.40
60 32i 1,102.12 1,547.29 445.17
61 32k 63.16 276.75 213.59
62 33i 232.81 1,091.84 859.03
63 34l 15,200.00 25,490.64 10,290.64
Total of area 1,412,500.00 1,412,500.00 0
-60000
-40000
-20000
0
20000
40000
60000
80000
1a 3c 6g 9c 9k 12d 13k 14k 15k 17g 18c 19c 21i 22k 24e 25c 27c 28d 29k 31k 32k
Loại cảnh quan
Diện tích (ha)
Các loại sinh thái cảnh quan
Figure 3.20: The area changes of LE kinds in Son La overtime
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Overlaping of LE maps in Son La province in 2005 and 2015 to identify
changes of LE kinds. The variation of LE kinds in Son La province during 2005 and
2015 is shown in Figure 3.20.
Area of some LE kinds increased from 2005 to 2015. The highest increase was
kind of 21i (different species plantation on Acric Ferrasols) with an increase of
55,862.06 ha because of increasing demand for agriculture cultivation; fowlowed by
kind of 14g (Scrubs and grasses on Ferralic Acrisols) with an area of 21,453.73
hectares, kind of 14i (different species plantation on Ferralic Acrisols) with an area
of 19,526.64 ha and kind of 29k (residential landuse on Orthic Ferralsols) with an
area of 12,867.36 ha. Increase of residential LE caused by population growth leading
to increase the habitat demand. The area of hydrology system increased significantly
with 10,290.64 ha. This is the result of the construction of the Son La hydroelectric
dam leading to an increase in the surface area of rivers and lakes in this province.
In contrast, some LE kinds have been decreased between 2005 - 2015. The
highest drop of LE kind was 7c (broadleaved forests on Chromic Ferralsols) with a
declined area of 52,924.32 ha, the second was kind of 18c (broadleaved forests on
Ferralsols) with a declined area of 37,969.90 ha and kind of 24c (broadleaved forests
on Chromic Ferralsols, in class of lowland and hillside) with an area of about
25,784.02 ha. SomeLE kinds are almost unchanged between 2005 and 2015 such as
kinds of 2g (Shrubs and grasses on Humic Alisols); 9e (mixed bamboo forests on
Ferralsols) and 5g (Shrubs and grasses on Humic Ferralsols).
Based on the research results, application of the GIS and database system, the
thesis edited the LE maps of Son La province in 2005 and 2015. The LE change in
Son La province from 2005 to 2015 was determined by overlaping the LE maps in
these two years. The LE changes show the trend of changing, which can identify the
natural and social impacts of Son La and support for a sustainable natural resources
management
3.4. The orientations of proper territory exploitation and use for socio-economic
development
General plan for socio-economic development of Son La province
Agriculture, forestry and aquaculture: Rapidly moving towards commodity
production; Establishing agro-industry- service-market linkages, ensuring sustainable
development and high efficiency in the future; establishing concentrated commodity
production areas; protecting watershed forests for hydroelectricity; developing farm
economy, considering the household economy as autonomous units; stabilizing and
increasing the production value of all sectors
Industry, handicrafts and construction: Transforming from agriculture economy
to econoy with high proportion of industry and services; exploiting potentials and
benefits from the Son La Hydropower Plant.
Toursim: Son La have potentials of tourism development with many kinds of
toursim activities. Thus, Son La should create tourism tours following ecotourism.
Spatial orientations of LE units for conservation and rational resourse usages
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The general viewpoints of these orientations based (1) the synthetic study of
natural conditions and natural resources, (2) the results of the landscape assessment
and the analysis of the development state of the agriculture, forestry, and toursm, and
(3) combination of reviewing the general plan of provincial socio-economic
development up to 2020 to propose an appropriate development orientation for Son
La province. The status and orientation of using the territory of Son La province is
shown in Table 3.6 and Figure 3.21.
Table 3.6. Status and orientations of territory use of Son La province
Kinds of LE
Area (ha) Characteristics
Current state of landuse
Services of LE kinds
Suggested orientation of
spatial conservation and
proper use of natural resources
13i, 14i, 15i, 16i, 17i, 21i, 22i, 29i, 30i, 31i, 32i, 33i
493,468.60 Low hills and mountain, quite flat, small slope ferrasols
Paddy field and annual crops
Providing food
- Maintain kinds of 13i, 14i, 21i; examine and select crops which are suitbale with the natural conditions and land slope of the locality - Increase the landuse efficiency - Prevent soil erosion, improve soil environment (22i)
13g, 14g, 17g, 22g, 29g, 32g
184,279.07 Low mountains and hills, Ferrasols.
Bushes and shrubs alternate with small size woody trees remaining after exploitation and bamboo
Provide land for expansion of agricultural cultivation and husbandry
- Widen area of wet rice cultivation in places having suitable conditions (14g) - Develop large livestock and poultry farms (32g) - Encourage people to plant forests and Green the bareland and hills (17g, 22g, 29g) - Develop protetion and production forets
8c, 9c,
178,128.98 Low mountains and hills; high
Bare land; and
Improve forest quality
- Forest protection and plantaion in
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Kinds of LE
Area (ha) Characteristics
Current state of landuse
Services of LE kinds
Suggested orientation of
spatial conservation and
proper use of natural resources
10c, 19c, 25c, 27c
slope; mild and huge amount of rainfalls; enough sunshine; deep soil thickness
Area of broadleaved forests declined
areas of 8c, 9c, 10c, 25c, 27c
9e, 11e, 18e, 23e, 24e, 25e, 26e, 27e
19,552.49 Low mountains and hills; high slope; mild and huge amount of rainfalls; enough sunshine; deep soil thickness
Areas of mix bamboo forests decreased
Natural ecological balance to improve the forest quality
- Forest protection and plantaion in areas of 9e, 11e, 18e, 25e, 26e, 27e
1a, 1b, 2g,
2,207.80 High mountain, highest peak is Pu Luông (2853 m); temperate climate and floras; high humidity due to condesation and little vaporation; Humic Alisols; high soil humidity; few running water flow; shallow soil layer and low soil nutrients
Coniferous forests, mixed coniferous-broadleaved forests and part of scrubes and grasses. There are some specious timber species
Protecting biodiversity; endemic and specious species; genetic keeping; water regulation; flood mitigation; environment protection and prevention of climate change
- In-situ LE kinds of 1a, 1b; - Forest rehabilitation on LE kind of 2g
3c, 4c, 7c, 18c, 24c,
5g, 6g
88,460.14 Average mountains, mean annual temperature from 10 - 15
oC,
cold season lasts ≥ 8 months, dry
Area of mixed broadleaved-coniferous forests, broadleaved limestone forests,
Protecting biodiversity; endemic and specious species; genetic keeping; water
- Develop tourism to adventure Karst caves (3c, 4c, 7c, 18c, 24c); - To develop tourism economy in combination with convalescent
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Kinds of LE
Area (ha) Characteristics
Current state of landuse
Services of LE kinds
Suggested orientation of
spatial conservation and
proper use of natural resources
season lasts 5 - 6 months; 0 - 3 month drought; rainfalls over 2.000 - 2.500 mm/year; Alisols
broadleaved deciduous and semi-deciduous forests; bushes and scrubs, shrubs on high and average mountain has been decreased, in which, the most declined is kind of 7c
regulation; flood mitigation; environment protection and prevention of climate change
tourism (3c, 4c, 7c, 18c, 24c); - Forest halibitation on LE kinds of 5g, 6g
9f, 18f, 19f, 20f, 24f
12,329.95 Cool weather, temperature of 15
oC - 20
oC, 4
- 7 month cold season, mid rainfalls with everage annual amount of 1.500 - 2.000 mm; 3 - 6 month dry season. Humic ferrasols
Plantation forests on low mountain and plateau.
Preventing soil erosion, flood, landslides; environment protection; regulation and production
- Forest plantation on kinds of 9f, 20f. - Prospose some woody species for plantation like: Chukrasia tabularis (Lát hoa); Cassia siamea (Muồng đen); Manglietia glauca (Mỡ); Acacia magnum (Keo lá tràm); Pinus kesiya (Thông 3 lá).
9k, 13k, 14k, 15k, 16k, 17k, 22k, 24k, 29k, 31k,
73,921.61 Valley and low terrain, flat, altitude of 25 - 900 m, average annual temperature over 20
oC,
average annual rainfalls < 2.000 mm,
Residental land, commercial and service development and industry zones
Develop socio-economics, urban and infrastructure development,
- Continuously develop these landscape kinds following their states to serve the production and the daily life of the local people - Urban development:
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Kinds of LE
Area (ha) Characteristics
Current state of landuse
Services of LE kinds
Suggested orientation of
spatial conservation and
proper use of natural resources
32k short cold seasons ≤ 4 months, dry season from 3 - 6 months
Rational development of big cities, towns and townships. - Check of urban development planning - Integrated investment in urban infrastructure - Develop wood processing industry, forestry services and raising the value of forestry products; - Raise awareness in environmental protection
34l 25,490.64 Incl. ponds, lakes, rivers and streams, growth of hygrophyte
Provide area of specialized surface water
Aquaculture, hydorpower, tourism, wáter way trasportation
- Protect and develop the Son La hydropower plant - Develop aquaculture and waterway transportation in potential areas - Develop tourims at the areas of the hydropower plant reservoir and beautiful streams and landscapes.
CONCLUSION AND RECOMMENDATION
CONCLUSION
1. The research classified LE system in Son La including: the tropical monsoon
climate LE system, sub system of monsoon tropical monsoon LE with mild
winters and a dry season. Four classes of LE includ: Mountain (SLI) with
649,884.78 ha; highland (SLII) with 253,894.66 ha; hills and lowland under
500m (SLIII) with 483,229.96 ha; rivers, streams, ponds, lakes (SLIV) with
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25,490.64 ha. Mountain LE class has 3 sub-classes and 7 types. Plateu LE class
has 1 sub-class, 3 types. LE class of hills and lowland less than 500m has 3 sub-
classes. LE class of streams, ponds and lakes has 1 class. In Son La territory, 33
sub-types and 63 kinds of LE are divided.
2. The research constructed the maps of LE in Son La from 2005 to 2015 with scale
of 1:100.000, and calculated the area of each LE kind and the changes of LE
between 2005-2015.
- Approximately 1,731.79 hectares of LE kinds were changed in a positive
direction (bare lands were converted into LE kind of plantation forests),
accounting for 0.12% of the area.
- Approximately 28,431.64 ha of LE kinds were changed in a negative direction
(closed evergreen forests were converted into bare land and grasslands),
accounting for 2.01% of the area.
- There is a strong fluctuation of 25,490.64 ha, accounting for 1.80% because of
the construction of the Son La hydroelectric dam. This type of LE kinds
significantly affects on the LE changes in Son La province from 2005 to 2015
as well as interaction between constituent components of LE.
3. Based on the natural characteristics, human ecology of each LE unit, the thesis
has proposed 6 groups to exploit, use and develop sustainably LE in Son La
province including: agriculture on the type SLII - k3; industry on the type SLII -
k1; development of protected areas on the type LI-k1. More detailed kinds of
business are proposed according to the characteristics of sub-type and kinds units.
RECOMMENDATION
1. To promote researches and access to LE in biodiversity conservation in order
to have better theoretical foundation.
2. To develop gradually a teaching plan of LE in biology and researches into the
establishment of protected areas in Vietnam.
THE NEW POINTS OF THE THESIS
- The classification system of landscape ecology in Son La province was built
based on the selective inheritance of landscape and ecology research results.
- The map of landscape ecology in Son La province with scale of 1:100 000 was
built
- Initial clarification of ecosystem service values is the basis for proposing
conservation space and rational use of resources.
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THESIS - RELATED PUBLICATIONS OF PHD. CANDIDATE STUDENT
1. Doãn Thị Trường Nhung, Hà Quý Quỳnh, 2015. Xây dựng hệ thống thông tin quản
lý đa dạng sinh học Khu bảo tồn thiên nhiên, lấy KBTTN Tà Xùa, tỉnh Sơn La làm ví
dụ. Báo cáo khoa học tại Hội nghị toàn quốc về Sinh thái và Tài nguyên sinh vật toàn
quốc lần thứ VI, 2015. NXB Khoa học tự nhiên và Công nghệ, tr. 764-772.
2. Hà Quý Quỳnh, Doãn Thị Trường Nhung, 2015. Ứng dụng công nghệ viễn thám và
GIS nghiên cứu biến đổi thảm thực vật Khu bảo tồn thiên nhiên Tà Xùa, Sơn La. Báo
cáo khoa học tại Hội nghị toàn quốc về Sinh thái và Tài nguyên sinh vật toàn quốc lần
thứ VI, 2015. NXB Khoa học tự nhiên và Công nghệ, tr. 1627-1635.
3. Hà Quý Quỳnh, Doãn Thị Trường Nhung, Chu Thị Ngọc, 2016. Ứng dụng phần
mềm MapEdit và GIS để xây dựng và hiển thị bản đồ trong máy định vị GPS Garmin
60.x phục vụ quản lý vườn quốc gia, lấy ví dụ tại Vườn Quốc gia Xuân Sơn, Phú Thọ.
Báo cáo khoa học tại Tuyển tập báo cáo Hội nghị khoa học và công nghệ “Đo đạc bản
đồ với ứng phó biến đổi khí hậu”. NXB Tài nguyên – Môi trường và Bản đồ Việt Nam.
Hà Nội, tr. 221-229.
4. Doãn Thị Trường Nhung, Hà Quý Quỳnh, 2016. Ứng dụng viễn thám và GIS để
nghiên cứu thảm thực vật lòng hồ thuỷ điện, lấy ví dụ hồ thuỷ điện Sơn La. Báo cáo
khoa học tại hội nghị khoa học địa lý toàn quốc lần thứ 7. NXB Khoa học tự nhiên và
Công nghệ. Hà Nội, tr.475-480.
5. Doãn Thị Trường Nhung, Hà Quý Quỳnh, Lê Quang Tuấn, 2017. Ứng dụng viễn
thám và GIS để nghiên cứu biến động STCQ tại tỉnh Sơn La. Báo cáo khoa học tại Hội
nghị toàn quốc về Sinh thái và Tài nguyên sinh vật toàn quốc lần thứ VII, 2017. NXB
Khoa học tự nhiên và Công nghệ, tr. 1890-1894.