Landscape type reflects the ecological status of the landscape “characterized by the mutual relationship between plant communities and soil types in the microbiological cycle, determining the material balance of the landscape through climatic and soil conditions combined with the impacts of human activities”.
Landscape type is used as the basic unit of assessment to serve the direction of use and landscape improvement measures.
This landscape classification system is used to plan land use on medium scale maps: 1/100,000 - 1/250,000 applied to a province, a region and scale maps: 1/500,000 - 1/1000,000 for regions, the whole country.
Table 3.3. Vietnam landscape classification system
Percentile level
Classification mark | Some examples | |
Landscape system | The characteristics of the natural zonal scale are determined by the position of the territory relative to the Sun and the rotation of the Earth around itself. | Tropical monsoon landscape system. |
Subsystem | Quantitative characteristics of the | - Landscape subsystem |
landscape | climate conditions are specified | affected by the season |
determined by the operation of the regime | frozen, moist by flora | |
atmospheric circulation | Himalayan plant - Dipterocarpaceae. | |
interaction between things | - Landscape subsystem | |
temperature and humidity conditions on a regional scale | cold, dry, characteristic climate | |
zone. It determines the existence and | by two Himalayan floras | |
development of populations | dry, moist Indo-Burmese. | |
Plants related to the flora ecosystem. | - Hot and humid climate landscape subsystem with 2 systems | |
typical plants | ||
Malay-Indonesian display. |
Maybe you are interested!
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Applied Geographic Landscape Part 2 - 2 -
Identify Rating Levels and Rating Scales
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zt2a3gstourism,quan lan,quang ninh,ecology,ecotourism,minh chau,van don,geography,geographical basis,tourism development,science
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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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Tourism Geography Part 1 - Hanoi College of Tourism - 2 -
Tourism Geography Part 1 - Hanoi College of Tourism - 20 -
Solutions for tourism development in Tien Lang - 10
zt2i3t4l5ee
zt2a3gstourism, tourism development
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- District People's Committees and authorities of communes with tourist attractions should support, promote, and provide necessary information to people, helping them improve their knowledge about tourism. Raise tourism awareness for local people.
*
* *
Due to limited knowledge and research time, the thesis inevitably has shortcomings. Therefore, I look forward to receiving guidance from teachers, experts as well as your comments to make the thesis more complete.
Chapter III Conclusion
Through the issues presented in Chapter II, we can come to some conclusions:
Based on the strengths of available tourism resources, the types of tourism in Tien Lang that need to be promoted in the coming time are sightseeing and resort tourism, discovery tourism, weekend tourism. To improve the quality and diversify tourism products, Tien Lang district needs to combine with local cultural tourism resources, at the same time combine with surrounding areas, build rich tourism products. The strengths of Tien Lang tourism are eco-tourism and cultural tourism, so developing Tien Lang tourism must always go hand in hand with restoring and preserving types of cultural tourism resources. Some necessary measures to support and improve the efficiency of exploiting tourism resources in Tien Lang are: strengthening the construction of technical facilities and labor force serving tourism, actively promoting and advertising tourism, and expanding forms of capital mobilization for tourism development.
CONCLUDE
I Conclusion
1. Based on the results achieved within the framework of the thesis's needs, some basic conclusions can be drawn as follows:
Tien Lang is a locality with great potential for tourism development. The relatively abundant cultural tourism resources and ecological tourism resources have great appeal to tourists. Based on this potential, Tien Lang can build a unique tourism industry that is competitive enough with other localities within Hai Phong city and neighboring areas.
In recent years, the exploitation of the advantages of resources to develop tourism and build tourist routes in Tien Lang has not been commensurate with the available potential. In terms of quantity, many resource objects have not been brought into the purpose of tourism development. In terms of time, the regular service time has not been extended to attract more visitors. Infrastructure and technical facilities are still weak. The labor force is still thin and weak in terms of expertise. Tourism programs and routes have not been organized properly, the exploitation content is still monotonous, so it has not attracted many visitors. Although resources have not been mobilized much for tourism development, they are facing the risk of destruction and degradation.
2. Based on the results of investigation, analysis, synthesis, evaluation and selective absorption of research results of related topics, the thesis has proposed a number of necessary solutions to improve the efficiency of exploiting tourism resources in Tien Lang such as: promoting the restoration and conservation of tourism resources, focusing on investment and key exploitation of ecotourism resources, strengthening the construction of infrastructure and tourism workforce. Expanding forms of capital mobilization. In addition, the thesis has built a number of tourist routes of Hai Phong in which Tien Lang tourism resources play an important role.
Exploiting Tien Lang tourism resources for tourism development is currently facing many difficulties. The above measures, if applied synchronously, will likely bring new prospects for the local tourism industry, contributing to making Tien Lang tourism an important economic sector in the district's economic structure.
REFERENCES
1. Nhuan Ha, Trinh Minh Hien, Tran Phuong, Hai Phong - Historical and cultural relics, Hai Phong Publishing House, 1993
2. Hai Phong City History Council, Hai Phong Gazetteer, Hai Phong Publishing House, 1990.
3. Hai Phong City History Council, History of Tien Lang District Party Committee, Hai Phong Publishing House, 1990.
4. Hai Phong City History Council, University of Social Sciences and Humanities, VNU, Hai Phong Place Names Encyclopedia, Hai Phong Publishing House. 2001.
5. Law on Cultural Heritage and documents guiding its implementation, National Political Publishing House, Hanoi, 2003.
6. Tran Duc Thanh, Lecture on Tourism Geography, Faculty of Tourism, University of Social Sciences and Humanities, VNU, 2006
7. Hai Phong Center for Social Sciences and Humanities, Some typical cultural heritages of Hai Phong, Hai Phong Publishing House, 2001
8. Nguyen Ngoc Thao (editor-in-chief, Tourism Geography, Hai Phong Publishing House, two volumes (2001-2002)
9. Nguyen Minh Tue and group of authors, Hai Phong Tourism Geography, Ho Chi Minh City Publishing House, 1997.
10. Nguyen Thanh Son, Hai Phong Tourism Territory Organization, Associate Doctoral Thesis in Geological Geography, Hanoi, 1996.
11. Decision No. 2033/QD – UB on detailed planning of Tien Lang town, Hai Phong city until 2020.
12. Department of Culture, Information, Hai Phong Museum, Hai Phong relics
- National ranked scenic spot, Hai Phong Publishing House, 2005. 13. Tien Lang District People's Committee, Economic Development Planning -
Culture - Society of Tien Lang district to 2010.
14.Website www.HaiPhong.gov.vn
APPENDIX 1
List of national ranked monuments
STT
Name of the monument
Number, year of decisiondetermine
Location
1
Gam Temple
938 VH/QĐ04/08/1992
Cam Khe Village- Toan Thang commune
2
Doc Hau Temple
9381 VH/QĐ04/08/1992
Doc Hau Village –Toan Thang commune
3
Cuu Doi Communal House
3207 VH/QĐDecember 30, 1991
Zone II of townTien Lang
4
Ha Dai Temple
938 VH/QĐ04/08/1992
Ha Dai Village –Tien Thanh commune
APPENDIX II
STT
Name of the monument
Number, year of decision
Location
1
Phu Ke Pagoda Temple
178/QD-UBJanuary 28, 2005
Zone 1 - townTien Lang
2
Trung Lang Temple
178/QD-UBJanuary 28, 2005
Zone 4 – townTien Lang
3
Bao Khanh Pagoda
1900/QD-UBAugust 24, 2006
Nam Tu Village -Kien Thiet commune
4
Bach Da Pagoda
1792/QD-UB11/11/2002
Hung Thang Commune
5
Ngoc Dong Temple
177/QD-UBNovember 27, 2005
Tien Thanh Commune
6
Tomb of Minister TSNhu Van Lan
2848/QD-UBSeptember 19, 2003
Nam Tu Village -Kien Thiet commune
7
Canh Son Stone Temple
2160/QD-UBSeptember 19, 2003
Van Doi Commune –Doan Lap
8
Meiji Temple
2259/QD-UBSeptember 19, 2002
Toan Thang Commune
9
Tien Doi Noi Temple
477/QD-UBSeptember 19, 2005
Doan Lap Commune
10
Tu Doi Temple
177/QD-UBJanuary 28, 2005
Doan Lap Commune
11
Duyen Lao Temple
177/QD-UBJanuary 28, 2005
Tien Minh Commune
12
Dinh Xuan Uc Pagoda
177/QD-UBJanuary 28, 2005
Bac Hung Commune
13
Chu Khe Pagoda
177/QD-UBJanuary 28, 2005
Hung Thang Commune
14
Dong Dinh
2848/QD-UBNovember 21, 2002
Vinh Quang Commune
15
President's Memorial HouseTon Duc Thang
177/QD-UBJanuary 28, 2005
NT Quy Cao
Ha Dai Temple
Ben Vua Temple
Tien Lang hot spring
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Morphological characteristics of emergence | - Special mountain landscape class | |
mandarin | of the great territorial terrain, decided | characterized by migration processes |
determine the processes of formation and | move the ditch, jungle | |
material component | evergreen | |
non-zonal characterized by | - High landscape layer | |
quantitative expression of balance | characterized by the | |
material, process of movement | surface migration process | |
matter, biomass, | + accumulation. | |
The intensity of the biological cycle of populations is consistent with ecological conditions determined by a combination of topographic and climatic factors. | - Hilly landscape layer characterized by surface movement processes + gullies. - Plain landscape layer - material accumulation. | |
- Coastal island landscape layer | ||
shore - the process of accumulation and migration | ||
transfer mixture | ||
Subclass | Morphometric characteristics | - Landscape subclass above |
landscape | terrain within the classroom, | alpine. |
represents the material balance between the morphometric characteristics of the terrain, the climatic characteristics and the characteristics of the plant community: biomass, growth rate, biological circulation according to the altitude thresholds. | - Medium mountain landscape subclass. - Low mountain landscape subclass. - Landscape layer on high plateau. - Landscape layer | |
coastal | ||
Landscape type | General bioclimatic characteristics determine the formation of vegetation types, the adaptive nature of plant population characteristics according to the fluctuating characteristics of the moisture-temperature balance. | - Tropical evergreen forest landscape, low mountain monsoon. - Tropical semi-deciduous forest landscape, low mountain monsoon. |
Scene class
Extreme bioclimatic characteristics determine the species composition of vegetation types, and define critical thresholds for the development of plant species that make up vegetation types according to their origin. | - Tropical evergreen forest landscape subtype, monsoon with a long cold season, short humid dry season. - Tropical semi-deciduous forest landscape subtype, monsoon with a long dry season, no cold winter. | |
Landscape type (group of types) | Characterized by the mutual relationship between plant communities and soil types in a microbiological cycle, determining the physical balance of the landscape through climatic and soil conditions, plus the effects of anthropogenic activities. | - Landscape type of evergreen broadleaf forest on red-yellow ferali soil on medium mountain shale. - Poor grassland shrub landscape on eroded, rocky hilly soil. |
Landscape subtype
(Pham Hoang Hai, Nguyen Thuong Hung, Nguyen Ngoc Khanh, 1997)
b. Landscape classification system of the authors of the Department of Natural Geography, Center for Geography and Natural Resources
In 1992, the authors of the Department of Natural Geography of the Center for Geography and Natural Resources proposed a landscape classification system for map scales in the work " Research on building landscape maps of scales on the territory of Vietnam" .
Classification system: Landscape system → landscape subsystem → landscape class → landscape subclass → landscape type → landscape subtype → landscape class → landscape type → landscape form →. landscape area.
In detailed territorial use planning (map scale 1/50,000 - 1/25,000), the selected basic landscape unit is the landscape type according to the above classification system.
“ Landscape form is a landscape morphological unit, characterized by a trend and intensity of material transformation through the properties of terrain forms and soil variations ” .
Landscape form is the secondary unit of landscape morphology.
On the basis of the uniformity of vegetation types, characteristics of bioclimatic conditions, soil types, terrain types arising from morphology and exogenous processes, geomorphological and geological signs, landscape types are distinguished according to factors such as slope, soil mechanical composition, and soil layer thickness.
Landscape form is the basic unit for assessing plant ecological adaptation, selecting plant species and applying land use and cultivation measures.
Table 3.4. Landscape classification system of the Department of Physical Geography (1992)
Percentile level
Classification mark | |
Landscape system | The dominant radiation background determines the zonality. The temperature-humidity regime determines the intensity of the matter and energy cycle. |
Landscape patrilineage | The monsoon circulation regime determines the redistribution of heat. - Humidity greatly affects the material cycle. |
Landscape class | The characteristics of large terrain blocks determine the uniformity of two major processes in the material cycle of erosion and accumulation. |
Landscape subclass | Internal stratification of the class. |
Landscape type | Bioclimatic characteristics (vegetation type - soil type). |
Landscape subtype | Extreme climate characteristics. |
Landscape class | Terrain type and current dynamics. |
Landscape type | Relative similarity of the geographical forms constituting the landscape (the combination of modern phylogenetic plant communities with soil type). |
Morphological structural units. | |
Landscape type (plant complex, soil complex). | |
Landscape area. | |
According to the applied landscape research direction, the ecological landscape classification system commonly applied today is:
+ Order of levels of thermo-humidity foundation: Ecological landscape system
→ Landscape ecology subsystem → Landscape ecology type → Landscape ecology subtype.
+ Order of levels of solid foundation: Ecological landscape layer →
Ecological landscape subclass → Ecological landscape class.
The matrix linking the two classification systems is Level → Ecolandscape Type → Ecolandscape Form.
Illustrative example
Applying the applied landscape research direction, the landscape classification system is applied in the doctoral thesis topic "Analysis of landscape structure and function to serve the orientation of rational use of the Ma River basin (Thanh Hoa province)" (Vu Van Duan, 2020):
a. The landscape classification system of the Ma River basin includes the following levels: Landscape system landscape subsystem landscape type landscape class landscape subclass landscape rank landscape type . This is the basis for establishing a 1:100,000 scale map of the research territory.
Landscape type is used as the basic unit of assessment to serve the orientation of rational use of the Ma River basin territory.
b. Classification signs of levels in the system
- Landscape system: The characteristics of this system are determined by the correlation between the geographical location and the solar radiation energy source that the territory receives. Because it is located within the Northern Hemisphere's tropical belt, the research territory belongs to the Southeast Asian tropical monsoon landscape system.
- Landscape subsystem: Located in the transitional zone between the tropical monsoon climate without cold winters in the South and
Tropical monsoon climate with cold winter in the North, Ma River basin territory is located in the interaction between terrain and Northeast monsoon, Southwest monsoon determines the redistribution of heat and humidity. With the characteristics of mountain structure, Ma River basin territory is determined to belong to the tropical monsoon landscape subsystem with the rhythm of summer-autumn rainy season, cold winter.
- Landscape type: Due to its high sensitivity to external conditions and the ability to preserve the properties of vegetation, there is a very close relationship between temperature and humidity conditions, the type of vegetation that arises, and the type of soil, and at the same time it is the basis for dividing landscape types. The research territory has 13 landscape types.
- Landscape layer: Is a level of territorial differentiation based on the difference in material balance due to the combination of terrain and climate factors, creating different intensities of biological circulation. Originating from the characteristics of morphological structure and topographic morphology, which determines the uniformity of two major processes in the material cycle of erosion and accumulation of plain, hill and mountain terrain types, it has influenced the non-zonal nature of the landscape layers in the study area. The territory of the Ma River basin belongs to 3 landscape layers: Plain landscape layer, hill landscape layer and mountain landscape layer.
- Landscape sub-layers: The stratification of natural conditions and processes in the high-altitude belt system has contributed to the formation of landscape sub-layers in the Ma River basin:
- Medium mountain CQ class.
- Low mountain CQ subclass.
- Subclass CQ valley, low-lying area.
- High hill CQ class assistant.
- Low hill CQ class.
- High plain CQ subclass.
- Lowland CQ subclass.
- Landscape class: Divided according to soil geomorphology and surface sediment geomorphology. Regarding geomorphology, these are landforms divided according to the principle of morphology and origin, the surface is composed of a type or combination of soil types, a combination of sedimentary materials. The research territory has 34 landscape classes.
- Landscape type: Is the result of the interaction between the thermal foundation
- moisture and solid ground; in which the factors: Terrain elevation, climate characteristics, soil type, soil layer thickness, terrain slope and current plant community are used as indicators when classifying landscapes. This is the basic level of importance in comprehensively assessing natural conditions as well as proposing rational use of the territory. Within the scope of the research territory, there are 348 landscape type units.
Table 3.5. Landscape classification system of Ma River basin
Classification level
Characteristic signs | CQ classification results | |
System | The dominant radiation background determines | - Tropical humid landscape system |
CQ | zonal. Humidity and temperature regime | monsoon |
determine the intensity of the cycle | ||
matter and energy | ||
Patriarchy | Correlation between terrain and wind | - The landscape patrilineal system has a rhythm of rainy summer-autumn season and cold winter. |
CQ system | Northeast monsoon | |
South decides redistribution | ||
heat and humidity | ||
Type | General bioclimatic characteristics | - The research territory has 13 |
CQ | determine vegetation type | landscape type |
emergence and adaptation of | ||
plant populations due to variation | ||
movement of heat and moisture balance. | ||
Class | Morphological characteristics of emergence | - Mountain landscape class |
CQ | of the great terrain, determining the | - Hill landscape class |
identity of two major processes in the cycle of material erosion | - Plains scene class | |
and accumulation. |
Characteristics of geometrical measurements | - Medium mountain CQ class | |
CQ | internal stratification | - Low mountain CQ sub-class |
of the landscape layer. Shows balance | - Valley CQ class, | |
by material between characteristics | depression | |
topographic survey, | - High hill CQ class | |
climate and characteristics | - Low hill CQ sub-class | |
characteristic of plant populations | - High plain CQ sub-class | |
- Lowland CQ sub-class | ||
Class | Divided by geographical indicators | The study area has 34 landscape categories. |
CQ | soil, geomorphology | |
surface area. In terms of topography it is | ||
terrain types are classified | ||
divided according to morphological principles- | ||
origin, on the surface is structured | ||
made up of a type or combination of | ||
soil, a combination of materials | ||
sediment | ||
CQ Type | The association of plant communities (groups) with soil types (groups) through human impacts. | The research territory has 348 landscape types (including 2 common types: water surface and residential). |
Subclass
(Vu Van Duan, 2020)
3.5. LANDSCAPE MAP ESTABLISHMENT
A new approach that has been widely used in recent years is to use landscape classification results in creating landscape maps in applied research projects.
Landscape maps are a product of comprehensive research, objectively reflecting the characteristics of nature, the relationships and interactions between natural components. This is an important basis for proposing plans for rational use of the territory.





