In order to determine the area, sustainability of genetic diversity, biomass and reserves of timber species, the scientific basis for forest sustainability in the thesis is the characteristics of forestry land, characteristics of existing forests and the fluctuations of these characteristics over space and time under the impact of the main factors of change and STR.
The main products of this study are: to determine the boundaries, divide and mark the functional zones and buffer zones of the national park; clearly demarcate the land area planned for purposes other than the area planned for the National Park for the harmonious development of forest protection, environmental protection, nature conservation and conservation of rare, precious and endangered wildlife species. Propose a process to guide the monitoring, inspection and supervision of forest resources and biodiversity in the National Park for the purpose of effectively conserving and preventing deforestation, encroachment and illegal conversion of the purpose of use of the National Park. However, with the content of the thesis topic, the main approach of the topic is: Applying geospatial technology in forest resource management in the National Park for the purpose of providing periodic and regular information on: (i). Deforestation and degradation of forest resources; (ii). New forest areas
This research topic has profound scientific and practical significance to overcome the shortcomings of previous studies, contributing to providing a technological process to ensure highly effective management and monitoring of forest resources.
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Identify Rating Levels and Rating Scales
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of the islanders. Therefore, this indicator will be divided into two sub-indicators:
a1. Natural tourism attractiveness a2. Cultural tourism attractiveness
b. Tourist capacity
The two island communes in Quan Lan have different capacities to receive tourists. Minh Chau Commune is home to many standard hotels and resorts, attracting high-income domestic and international tourists. Meanwhile, Quan Lan Commune has many motels mainly built and operated by local people, so the scale and quality are not high, and will be suitable for ordinary tourists such as students.
c. Time of exploitation of Quan Lan Island Commune:
Quan Lan tourism is seasonal due to weather and climate conditions and festivals only take place on certain days of the year, specifically in spring. In Quan Lan commune, the period from April to June and from September to November is considered the best time to visit Quan Lan because the cultural tourism activities are mainly associated with festivals taking place during this time.
Minh Chau island commune:
Tourism exploitation time is all year round, because this is a place with a number of tourist attractions with diverse ecosystems such as Bai Tu Long National Park Research Center, Tram forest, Turtle Laying Beach, so besides coming to the beach for tourism and vacation in the summer, Minh Chau will attract research groups to come for tourism combined with research at other times of the year.
d. Sustainability
The sustainability of ecotourism sites in Quan Lan and Minh Chau communes depends on the sensitivity of the ecosystems to climate changes.
landscape. In general, these tourist destinations have a fairly high level of sustainability, because they are natural ecosystems, planned and protected. However, if a large number of tourists gather at certain times, it can exceed the carrying capacity and affect the sustainability of the environment (polluted beaches, damaged trees, animals moving away from their habitats, etc.), then the sustainability of the above ecosystems (natural ecosystems, human ecosystems) will also be affected and become less sustainable.
e. Location and accessibility
Both island communes have ports to take tourists to visit from Van Don wharf:
- Quan Lan – Van Don traffic route:
Phuc Thinh – Viet Anh high-speed boat and Quang Minh high-speed boat, depart at 8am and 2pm from Van Don to Quan Lan, and at 7am and 1pm from Quan Lan to Van Don. There are also wooden boats departing at 7am and 1pm.
- Van Don - Minh Chau traffic route:
Chung Huong high-speed train, Minh Chau train, morning 7:30 and afternoon 13:30 from Van Don to Minh Chau, morning 6:30 and afternoon 13:00 from Minh Chau to Van Don.
f. Infrastructure
Despite receiving investment attention, the issue of infrastructure and technical facilities for tourism on Quan Lan Island is still an issue that needs to be resolved because it has a direct impact on the implementation of ecotourism activities. The minimum conditions for serving tourists such as accommodation, electricity, water, communication, especially medical services, and security work need to be given top priority. Ecotourism spots in Minh Chau commune are assessed to have better infrastructure and technical facilities for tourism because there are quite complete and synchronous conditions for serving tourists, meeting many needs of domestic and foreign tourists.
3.2.1.4. Determine assessment levels and assessment scales
Corresponding to the levels of each criterion, the index is the score of those levels in the order of 4, 3, 2, 1 decreasing according to the standard of each level: very attractive (4), attractive (3), average (2), less attractive (1).
3.2.1.5. Determining the coefficients of the criteria
For the assessment of DLST in the two communes of Quan Lan and Minh Chau islands, the students added evaluation coefficients to show the importance of the criteria and indicators as follows:
Coefficient 3 with criteria: Attractiveness, Exploitation time. These are the 2 most important criteria for attracting tourists to tourism in general and eco-tourism in particular, so they have the highest coefficient.
Coefficient 2 with criteria: Capacity, Infrastructure, Location and accessibility . Because the assessment area is an island commune of Van Don district, the above criteria are selected by the author with appropriate coefficients at the average level.
Coefficient 1 with criteria: Sustainability. Quan Lan has natural and human-made ecotourism sites, with high biodiversity and little impact from local human factors. Most of the ecotourism sites are still wild, so they are highly sustainable.
3.2.1.6. Results of DLST assessment on Quan Lan island
a. Assessment of the potential for natural tourism development
For Minh Chau commune:
+ Natural tourism attractiveness is determined to be very attractive (4 points) and the most important coefficient (coefficient 3), so the score of the Attractiveness criterion is 4 x 3 = 12.
+ Capacity is determined as average (2 points) and the coefficient is quite important (coefficient 2), then the score of Capacity criterion is 2 x 2 = 4.
+ Exploitation time is long (4 points), the most important coefficient (coefficient 3) so the score of the Exploitation time criterion is 4 x 3 = 12.
+ Sustainability is determined as sustainable (4 points), the important coefficient is the average coefficient (coefficient 1), so the score of the Sustainability criterion is 4 x 1 = 4 points
+ Location and accessibility are determined to be quite favorable (2 points), the coefficient is quite important (coefficient 2), the criterion score is 2 x 2 = 4 points.
+ Infrastructure is assessed as good (3 points), the coefficient is quite important (coefficient 2), then the score of the Infrastructure criterion is 3 x 2 = 6 points.
The total score for evaluating DLST in Minh Chau commune according to 6 evaluation criteria is determined as: 12 + 4 + 12 + 4 + 4 + 6 = 42 points
Similar assessment for Quan Lan commune, we have the following table:
Table 3.3: Assessment of the potential for natural ecotourism development in Quan Lan and Minh Chau communes
Attractiveness of self-tourismof course
Capacity
Mining time
Sustainability
Location and accessibility
Infrastructure
Result
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
CommuneMinh Chau
12
12
4
8
12
12
4
4
4
8
6
8
42/52
Quan CommuneLan
6
12
6
8
9
12
4
4
4
8
4
8
33/52
b. Assessment of the potential for humanistic tourism development
For Quan Lan commune:
+ The attractiveness of human tourism is determined to be very attractive (4 points) and the most important coefficient (coefficient 3), so the score of the Attractiveness criterion is 4 x 3 = 12.
+ Capacity is determined to be large (3 points) and the coefficient is quite important (coefficient 2), then the score of the Capacity criterion is 3 x 2 = 6.
+ Mining time is average (3 points), the most important coefficient (coefficient 3) so the score of the Mining time criterion is 3 x 3 = 9.
+ Sustainability is determined as sustainable (4 points), the important coefficient is the average coefficient (coefficient 1), so the score of the Sustainability criterion is 4 x 1 = 4 points.
+ Location and accessibility are determined to be quite favorable (2 points), the coefficient is quite important (coefficient 2), the criterion score is 2 x 2 = 4 points.
+ Infrastructure is rated as average (2 points), the coefficient is quite important (coefficient 2), then the score of the Infrastructure criterion is 2 x 2 = 4 points.
The total score for evaluating DLST in Quan Lan commune according to 6 evaluation criteria is determined as: 12 + 6 + 6 + 4 + 4 + 4 = 36 points.
Similar assessment with Minh Chau commune we have the following table:
Table 3.4: Assessment of the potential for developing humanistic eco-tourism in Quan Lan and Minh Chau communes
Attractiveness of human tourismliterature
Capacity
Mining time
Sustainability
Location and accessibility
Infrastructure
Result
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Point
DarkMulti
Quan CommuneLan
12
12
6
8
9
12
4
4
4
8
4
8
39/52
Minh CommuneChau
6
12
4
8
12
12
4
4
4
8
6
8
36/52
Basically, both Minh Chau and Quan Lan localities have quite favorable conditions for developing ecotourism. However, Quan Lan commune has more advantages to develop ecotourism in a humanistic direction, because this is an area with many famous historical relics such as Quan Lan Communal House, Quan Lan Pagoda, Temple worshiping the hero Tran Khanh Du, ... along with local festivals held annually such as the wind praying ceremony (March 15), Quan Lan festival (June 10-19); due to its location near the port and long exploitation time, the beaches in Quan Lan commune (especially Quan Lan beach) are no longer hygienic and clean to ensure the needs of tourists coming to relax and swim; this is also an area with many beautiful landscapes such as Got Beo wind pass, Ong Phong head, Voi Voi cave, but the ability to access these places is still very limited (dirt hill road, lots of gravel and rocks), especially during rainy and windy times; In addition, other natural resources such as mangrove forests and sea worms have not been really exploited for tourism purposes and ecotourism development. On the contrary, Minh Chau commune has more advantages in developing ecotourism in the direction of natural tourism, this is an area with diverse ecosystems such as at Rua De Beach, Bai Tu Long National Park Conservation Center...; Minh Chau beach is highly appreciated for its natural beauty and cleanliness, ranked in the top ten most beautiful beaches in Vietnam; Minh Chau commune is also home to Tram forest with a large area and a purity of up to 90%, suitable for building bridges through the forest (a very effective type of natural ecotourism currently applied by many countries) for tourists to sightsee, as well as for the purpose of studying and researching.
Figure 3.1: Thenmala Forest Bridge (India) Source: https://www.thenmalaecotourism.com/(August 21, 2019)
3.2.2. Using SWOT matrix to evaluate Quan Lan island tourism
General assessment of current tourism activities of Quan Lan island is shown through the following SWOT matrix:
Table 3.5: SWOT matrix evaluating tourism activities on Quan Lan island
Internal agent
Strengths- There is a lot of potential for tourism development, especially natural ecotourism and humanistic ecotourism.- The unskilled labor force is relatively abundant.- resource environmentunpolluted, still
Weaknesses- Poorly developed infrastructure, especially traffic routes to tourist destinations on the island.- The team of professional staff is still weak.- Tourism products in general
quite wild, originalintact
general and DLST in particularalone is monotonous.
External agents
Opportunity- Tourism is a key industry in the socio-economic development strategy of the province and Van Don economic zone.- Quan Lan was selected as a pilot area for eco-tourism development within the framework of the green growth project between Quang Ninh province and the Japanese organization JICA.- The flow of tourists and especially ecotourism in the world tends toincreasing
Challenge- Weather and climate change abnormally.- Competition in tourism products is increasingly fierce, especially with other localities in the province such as Ha Long, Mong Cai...- Awareness of tourists, especially domestic tourists, about ecotourism and nature conservation is not high.
Through summary analysis using SWOT matrix we see that:
To exploit strengths and take advantage of opportunities, it is necessary to:
- Diversify products and service types (build more tourism routes aimed at specific needs of tourists: experiential tourism immersed in nature, spiritual cultural tourism...)
- Effective exploitation of resources and differentiated products (natural resources and human resources)
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Current Status of Soc Son Protective Forest Resources for Tourism Purposes -
Research and propose solutions for community forest management in Ngan Son - Bac Kan - 2 -
Structural Characteristics of the Forest Stand with Distribution of 5-Needle Pine -
Research on resources, current situation, and solutions to exploit the humanistic ecological tourism route in Hai Duong. Building the route Hanoi - Cam Giang - Thanh Mien - Ninh Giang - Chi Linh - Hai Duong City - 8
Chapter 2
CONTENT, METHODS AND CHARACTERISTICS OF THE RESEARCH AREA
2.1. Research content
2.1.1. Research on the current characteristics of forest resources and factors affecting forest resource management in the NKD National Park area
a. Current characteristics of forest resources:
b. Factors affecting forest resource management:
c. Infrastructure for applying geospatial technology in forest resource management in the NKD National Park area
2.1.2. Research on the application of remote sensing index thresholds in early detection of deforestation and forest degradation in the NKD National Park area
a. Building a data set on deforestation and forest degradation:
b. Determine the remote sensing index threshold
c. Verify results
2.1.3. Research on the application of remote sensing index thresholds in detecting areas with new forests in the NKD National Park area
a. Build a data set of areas with new forests:
b. Determine the remote sensing index threshold
c. Verify results
2.1.4. Research proposes some solutions to promote the application of geospatial technology in forest resource management at NKD National Park
a. Proposing a process for applying geospatial technology in early detection of deforestation, forest degradation and new forest areas in the NKD National Park area
b. Propose some measures to support improving the effectiveness of using geospatial technology in forest resource management at the National Park.
c. Propose solutions to improve the effectiveness of forest protection management in the study area.
2.2. Research method
2.2.1. Methodology
One of the important products of the thesis is to propose solutions to promote the application of geospatial technology in forest resource management in the research area and can be applied and replicated in other areas with similar conditions to the research area.
(1). Scientific basis
The scientific basis of optical remote sensing data is the spectral reflectance of natural objects, which can be analyzed and displayed, especially detecting and separating deforested areas with separate areas. Based on the spectral reflectance characteristics of the objects, using specialized models and software, remote sensing data is processed to identify and separate each object. Multi-temporal remote sensing data allows for rapid determination of changes in forest cover in general and deforestation in particular during the time between image acquisition times. Information about forest objects after extraction can create status maps and calculate specific areas at each time as well as synthesize and analyze the results of distribution and changes.
The ARVI vegetation index represents the quality of green vegetation on the ground, the value of this index ranges from -1 to +1, the higher the value, the denser the vegetation. For forests, this index is quite high (about 0.6 to 1), when this value decreases, it means that vegetation is lost, or in other words, the forest is lost. Similarly, for other vegetation indices, the value of the index will represent the quality of vegetation in one way or another. On remote sensing images, the ARVI value is calculated for each pixel,
Therefore, for each area identified as deforested, degraded, or added forest, the number of pixels in that area can be calculated, or in other words, the area of lost, degraded, and newly added forest can be completely indicated because each pixel has a specific size and this parameter depends on the image data used for calculation.
Within the framework of this study, based on the above methodology, the process of identifying and expressing changes in deforestation, degradation and forest addition has been developed. Based on research, surveying the current status, monitoring changes and impacts of the change processes, managers can propose management solutions, protection planning, and restoration for sustainable development.
(2) Key terms used in the thesis
According to the explanation of the terms of the Lao Forestry Law. In this thesis, some important terms including: deforestation, forest degradation, new forest area need to be clarified. Through the terms used, readers can see some research issues that have been limited by the author to suit the author's research capacity, as well as to have a basis for reviewing and evaluating the results of the thesis.
- Deforestation: the forest is cut down, the forest vegetation layer is exploited, leaving a canopy cover of less than 0.1 (lower than the threshold for forest currently applied in Laos);
- Forest degradation: the forest is affected by: selective logging, thinning, forest fires, livestock grazing, etc., reducing the reserve and canopy cover of the forest compared to the original state, before being impacted;
- Area with new forest: Area of forest planting and forest restoration that has met the standards of becoming a forest from areas without forests or with vegetation but not meeting the criteria of becoming a forest (according to the definition of forest in Laos).
(3) Selection of technology and research materials
a) Technology:
- Geospatial technology including (global positioning system, geographic information system and remote sensing) are tools used throughout the contents of the thesis. In addition, the thesis also used statistical analysis tools to analyze data. Specifically as follows:
40
- Global Positioning System (GPS): GPS was used in the field survey of standard plots to determine basic indicators of forest structure and volume. The survey standard plots were located at the center coordinates of the plots, then the coordinates of the standard plots were transferred from GPS to ArcGIS software to extract remote sensing index values on satellite images. In addition, GPS was also used to locate the coordinates of newly added forest samples, deforestation, and forest degradation. GPS will be a useful tool for verifying the results of detecting deforestation, forest degradation, and newly added forest areas from applying the research results of the thesis into practice in the NKD National Park area.
- Geographic information system (GIS): ArcGIS 10.3 is the main software used in the thesis. The sampling of new forests, deforestation, forest degradation and some other operations were performed on the software. With data in Raster format (remote sensing images) was performed on ArcGIS software. Remote sensing images, immediately after being downloaded to the computer, will be cropped according to the research scope on ArcGIS software. Other operations are also performed on this software such as: calculating KB values, extracting values of remote sensing indicators on images, classifying Raster files according to thresholds to determine deforestation areas, forest degradation, etc.
- Remote sensing (RS). ARVI remote sensing index and Sentinel 2 satellite images were used in the thesis. Some tasks related to satellite images were performed by the author in GEE such as: calculating ARVI images; retrieving information of image scenes (image scene name, shooting time, cloud ratio); extracting ARVI values according to sample areas; downloading satellite images to the computer for analysis in GIS. Setting the pixel values on the image to zero was also performed on GEE. GEE is a powerful image analysis program today, although it is more difficult to perform than some other image processing software because it requires knowing how to manipulate code, but with the research content of the thesis, choosing GEE is appropriate.
41
- Planet.com has been used in the thesis. This is a Web tool that provides high-resolution satellite images from 3-5 m in 2 forms, commercial and free for some units, individual researchers/educators. Planet also supports users to be able to bring in areas according to boundaries (in .KML file format) to view with 2 screen windows corresponding to 2 time points (day, month, year) that the user chooses. Therefore, this is a useful tool that the author has used to verify the patterns of unchanged forests, deforestation, forest degradation and forest addition as a basis for selecting research samples.
b) Select research data
- Using Sentinel 2 images in research:
Sentinel 2 satellite images (spatial resolution 10, 20, 60 m) were selected for research because these are 2 of the types of optical images with medium and low resolution that are being exploited for free from image providers. Sentinel 2 satellite images were downloaded by the thesis from the Google Earth Engine program.
- Using ARVI index in research:
Experience in the world, in Vietnam as well as in Laos shows that almost no remote sensing index (NDVI; NBR; SAVI; ARVI; IRSI; NDSI; EVI) has outstanding advantages over other indexes in all conditions. Therefore, the application of remote sensing indexes depends on the specific conditions of each region as well as the existing measurement database system in that region.
In this thesis, the application of the ARVI index is studied. Unlike other vegetation indices, ARVI is very effective against topographic and atmospheric effects, which makes it a quality monitoring tool for tropical mountainous areas in developing countries where the concentration of suspended matter (rain, fog, dust, smoke, pollution) in the air is high. Therefore, ARVI is very suitable for monitoring complex terrain and many human impacts such as the area around the NKPNP. Moreover, in addition to the indices already
researched by other authors, the application of this index by the relative index method to the research area will achieve high results, with higher testing accuracy. From there, it contributes to the theoretical and practical basis for the application of ARVI, KB index in particular and CNĐKG in general for forest monitoring, early detection of deforestation, forest degradation, and areas with new forests in Laos.
Applying the thesis's thesis, the research approach flow diagram of the thesis topic is shown below (Figure 2.1).

Figure 2.1. Logical framework of research process
+ Step 1: Determine the area of forest types, area, location of lost, degraded and newly added forests as well as some structural indicators through the 86 OTC system arranged in the field. The causes of difficulties in resource management and deforestation and forest degradation in the area are determined through sociological investigation. The main results of step 1 serve as the premise and basis for step 2.
+ Step 2: Select geospatial technology, remote sensing images and remote sensing indices, calculate and establish appropriate thresholds to detect deforestation, forest degradation and forest addition in reality that have been determined.
+ Step 3: Analyze the ARVI index on the image to determine the index threshold showing deforested areas, degraded forests and newly forested areas. Use actual sample points in the field (threshold samples) to accurately determine the locations of the analyzed areas on the image, and get the analysis value.
+ Step 4: Verify the threshold results. Use actual sample points in the field (different from the threshold samples) according to each index threshold for each object: deforested bare land, degraded forest and newly forested areas, thereby assessing the accuracy of the method.
+ Step 5: The thesis proposes and orients the application of geospatial technology in forest resource management in Nam Ka Dinh National Park.
2.2.2. Research method
2.2.2.1. Content 1: Methods of investigation and assessment of the current status of resources and basic characteristics of some forest types
(i). Determine the forest type/forest status distributed in the NKD National Park area:
Forest type/status is determined according to the classification system stipulated in the Lao Forestry Law 2019 (National Assembly, 2019) [45]. According to Article 16, Clause 7, points a, b, c, d. Forest type is classified according to tree species composition and forest status is classified based on forest reserves (rich, medium, poor, depleted forests, forests with no reserves) (similar to Circular 33/2018/TT-BNNPTNT).
(ii). Method of determining characteristics of forest states
To collect full characteristics of forest structure and status, the thesis conducts survey lines. The survey lines are typical lines (typical according to forest type), representative of forest types, the length of the lines is not determined (according to the length of the forest type). On each line, a number of standard plots (OTC) are established as sample points for the survey. The sequence of steps to establish lines, sample points and conduct field surveys, and measure research indicators is carried out in the following steps.
Preliminary determination of the number of routes, drawing routes on the current distribution map and establishing standard plots according to forest type





