D t /D 1.3 for Acacia mangium stands of different ages in Ham Yen. The results are summarized in Table 4.6:



Table 4.6 : Equations expressing the relationship D t /D 1.3 in the form: D t = a + bD 1.3 at different ages
Year old
Equation of relationship H/D | R | Probability of the standard | |||
P(Fr) | P(t a ) | P(t b ) | |||
3 | Dt = 1.001 + 0.162.D 1.3 | 0.79 | 0.000 | 0.000 | 0.000 |
4 | Dt = 0.8547 + 0.1489.D 1.3 | 0.84 | 0.000 | 0.000 | 0.000 |
5 | Dt = 0.723 + 0.1676.D 1.3 | 0.81 | 0.000 | 0.000 | 0.000 |
6 | Dt = 0.3133 + 0.1883.D 1.3 | 0.80 | 0.000 | 0.028 | 0.000 |
7 | Dt = 0.5457 + 0.1723.D 1.3 | 0.81 | 0.000 | 0.002 | 0.000 |
8 | Dt = 0.0576 + 0.1893.D 1.3 | 0.84 | 0.000 | 0.725 | 0.000 |
9 | Dt = 0.6077 + 0.1514.D 1.3 | 0.76 | 0.000 | 0.000 | 0.000 |
10 | Dt = 0.811 + 0.1195.D 1.3 | 0.81 | 0.000 | 0.000 | 0.000 |
11 | Dt = 0.6173 + 0.1812.D 1.3 | 0.86 | 0.000 | 0.002 | 0.000 |
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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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Absolute growth rate of experimental chickens over weeks of age






From Table 4.6, it can be seen that the correlation coefficient R fluctuates from 0.76 to 0.86. There are 1/9 cases with P(t a ) > 0.05, meaning that the regression parameter a does not exist. All 9 cases have P(Fr) and P(t b ) < 0.05, meaning that the correlation coefficient R and the regression parameter b exist. The correlation equation actually exists, between D t and D 1.3 there is a relationship at the level of cutting. From there, through D 1.3 (an easily measurable indicator), it is possible to determine the canopy diameter of the trees in the forest stand, thereby determining the appropriate nutritional area, the optimal density for the current forest stand and the appropriate forest maintenance cutting intensity. At the same time, it is also possible to choose appropriate silvicultural measures to regulate the canopy, increasing the growth rate of forest trees.
4.0
3.5
3.0
2.5
Dt/D correlation chart 1.3 (age 4)
DT
Dt/D correlation chart 1.3 (age 6)
DT
6
5
4
3
2.0
1.5
6 8
D
10 12
14 16
Observed Linear
2
1
8 10
D
12 14
16 18
20 22
Observed Linear
24
5.0
4.5
4.0
3.5
3.0
Correlation chart Dt/D 1.3 (age 8)
DT
4.5
4.0
3.5
3.0
Dt/D correlation chart 1.3 (age 10)
DT
2.5
2.0
1.5
1.0
8 10
D
12 14
16 18 20 22
Observed Linear
24
2.5
2.0
1.5
0 10 20
D
Observed Linear
30
Figure 4.8 : Correlation chart D t /D 1.3 at ages 4, 6, 8, 10
Through table 4.6, it can be seen that the slope coefficient b of the equations varies from 0.1195 to 0.1893, so it is possible to hypothesize the homogeneity between ages, that is, to test the ability to establish a common equation for the research object to quickly determine the canopy diameter through the diameter at breast height without knowing the history of the Acacia mangium lot (age).
At the same age, the forest stands have been tested for the homogeneity of the investigated factors (D 1,3 , H vn , D t ) so it is only necessary to test the homogeneity of the correlation equations D t /D 1,3 of the form (3.6) at 9 different ages using Pearson's 2 standard . The calculation formula is:
n 2
n
2 W
W bi . b i
. b 2 i 1
n
(4.3)
b
i 1
ball
n
W ball
i 1
With W bi being the weight of the regression coefficient b i and W bi = 1/Sb i 2 ; where Sb i 2 is the variance of the regression coefficient b i . If 2 is calculated 05 2 and the table with k = n-1 degrees of freedom is consulted, then the regression coefficients b i are homogeneous, meaning that the hypothesis H 0 is accepted, then the simple linear regression equations will be combined into a common equation.
After establishing the correlation equations at different ages, check the homogeneity of the regression coefficients b i . The results show that 2 = 56.05 > 2 05
= 15.5 (with k = 8). Thus, it is not possible to determine a general equation expressing the relationship D t /D 1.3 for all Acacia mangium stands of different ages. In other words, it is only possible to use the equation expressing the relationship D t /D 1.3 for each age in Acacia mangium stands.
4.1.7. Correlation rule between volume of barkless tree trunk and diameter
and tree height (V kv /D 1.3 /H vn )
Volume is an important factor and the target of forest resource investigation. Like other factors, there is always a close relationship between the volume of the barkless tree trunk and the diameter and height of the tree trunk, expressed in many different mathematical equations. The topic will test some popular equations, used by many domestic and foreign experts. The tested equations are in the form: (3.7), (3.8), (3.9), (3.10).
To establish the relationship between the volume of the barkless tree trunk and the diameter and height of the tree trunk, the study used data from 16 analytical trees (including 144 trees from 2 to 10 years old). The processing results are summarized in table (4.7) as follows:
Table 4.7 : Summary of parameters when analyzing regression and correlation
of function forms
PT form
R 2 | S 2 y | a | b | c | |
(3.7) | 0.9929 | 6.88E-5 | 1,234E-03 | 3.89E-05 | |
(3.8) | 0.9929 | 6.93E-5 | 8,917E-04 | 3.35E-05 | 3.88E-05 |
(3.9) | 0.9932 | 6.68E-5 | 3.19E-5 | 1,839214 | 1,21037 |
(3.10) | 0.9503 | 1.18E-3 | 0.128624 | 5,951E-5 |
Note: R 2 has been linearized.
Table 4.7 shows that all four equations give very high coefficients of determination and small regression variances. This shows that there is a very close relationship between the volume of the barkless tree trunk and the height and diameter of the tree trunk.
y
Of the four equations above, form (3.9) has the highest coefficient of determination (R 2 = 0.9932) and the smallest regression variance (S 2 = 6.68E-5). Therefore, the topic decided to choose function (3.9) to describe the relationship between the volume of the barkless tree trunk and the diameter and height of the tree trunk. The specific equation is:
V = 3.19E-5.D 1.839214 .H 1.21037 (4.4)
4.1.7.1. Checking systematic errors of the V/D/H relation equation
To select a suitable regression equation to represent the V/D/H relationship, in addition to relying on statistical indicators such as coefficient of determination, regression variance, ... the topic uses the currently popular standard and has also been included in SPSS software, the Durbin - Watson d standard to check the systematic error of equation (4.4). This standard has the formula:
2
e i e i 1
i
d e 2
(4.5)
In which: the sum sign in the numerator runs from 2 to n because an observation point is lost when taking the difference of successive observations. And the sum in the denominator is QE in the table.
^ 2
analysis of variance with
QE y y
. Range for accepting the null hypothesis H 0
There is no negative or positive autocorrelation or no systematic error as follows:
Assume
Decision | Limit | |
No positive autocorrelation | Reject | 0 < d < G d |
No positive autocorrelation | No conclusion | G d < d < G t |
No negative autocorrelation | Reject | 4-G d < d < 4 |
No negative autocorrelation | No conclusion | 4-G t < d < 4-G d |
No negative and positive autocorrelation | No rejection | G t < d < 4-G t |
In which: G t and G d are looked up in table [29] corresponding to n being the sample size, k being the number of independent variables with significance level = 0.05.
The advantage of this method of calculating systematic errors is that it does not require additional survey capacity beyond the sample capacity of the equation to check. In addition, the calculation is simple and accurate. But the disadvantage is that there are some regions that cannot be concluded.
The result of checking equation (4.4) is d = 1.843. With n = 144, k = 2, looking up the table, we get G d = 1.076 and G t = 1.760. Thus, d is in the range G t < d < 4-G t, which means that the equation does not have negative or positive autocorrelation, or in other words, the equation does not have systematic errors.
4.1.7.2. Check the suitability of the V/D/H relationship equation
To test the accuracy of formula (4.4), the topic used the calculated data of 28 felled trees (from age 4 to age 10) that did not participate in the equation establishment process. The data of these felled trees were inherited from Ham Yen Forestry and analyzed in 2006. By the method of determining the error
V expression V observe
V observe
The relative (∆%) between the actual volume of the tree trunk and the volume obtained from the value of D 1.3 , H vn of the tree is calculated using formula (4.4):
v %
*100
(4.6)
The test results show that: the relative error ranges from 0.1% to 18.62%, the average relative error is 8.75%, less than 10% (which is the allowable relative error in forest survey), the number of positive errors is 17, the number of negative errors is 11. This proves that formula (4.4) has the necessary accuracy. This equation can be used to determine the volume of each individual Acacia mangium tree or forest stand in the research area.
4.1.7.3. Correlation between volume of barked tree trunk and volume of barkless tree trunk
From formula (4.4) the volume of the tree trunk can be determined, however, it is only the volume of the tree trunk without bark. To determine the volume of the tree trunk with bark, the topic conducts a study on the relationship between the volume of the tree trunk with bark and without bark for Acacia mangium in the research area.
From the data of V cv and V kv of 44 felled trees of different ages, site conditions and densities. Of which: 16 felled trees at the age of 10, combined with the inherited data of Ham Yen Forestry, there are 28 trees at the ages from 4 to 10. Through the chart to detect the rule shown in figure (4.9):
etc
0.45
0.4
0.35
0.3
0.25
0.2
0.15
0.1
0.05
0
0
0.1
0.2
0.3
VK
0.4
Figure 4.9 : Diagram showing the relationship between V cv and V kv
Based on the above point cloud diagram, the topic has established the relationship between the volume of the barked tree trunk and the volume of the barkless tree trunk through the form of a straight line relationship. The calculation results on Excel are specifically expressed in the following equation:
V cv = 0.008867 + 1.077386.V kv (4.7)
The correlation coefficient of the equation is very high (R = 0.996), the regression standard error is small (S y = 0.00894). The regression coefficients a and b both exist (because there is probability P(a)
= 2.47E-03 and P(b) = 6.16E-46 are both less than 0.05). Thus, the relationship between
The correlation between the volume of a tree trunk without bark and the volume with bark is very close. In other words, determining the volume of a tree trunk with bark from the volume of a tree trunk without bark (or vice versa) is appropriate and gives high accuracy.
4.1.8. Relationship between regular geometry (f 1.3 ) and tree trunk diameter and height
Shape is an important factor in the volume of a tree trunk but cannot be measured directly on the tree like its diameter or height. Therefore, understanding shape has special significance in the theory and practice of tree measurement.
The purpose of determining the shape is to calculate the volume of a standing tree trunk, so it is not possible to use known conceptual formulas and calculation formulas for this purpose. The shape on a standing tree trunk can only be determined through its relationship with easily measurable factors on the trunk.
When determining the forest reserve, it is possible to study to find an average numerical value for use in calculations that will be simpler while still ensuring accuracy. However, this value will deviate from the actual value of each individual tree. Based on the above reasons, to solve the problem of determining f 1.3 for each individual tree, the topic conducts research on its relationship with easily measured factors on the tree trunk, which are d 1.3 and h vn .
The research material is the 10-year-old trees (planted forest in 2005).
1997), with a sample size of 16 trees, it is sufficient to calculate the characteristics.
necessary sample. Because according to Dong Sy Hien (1974) [10], when studying the shape of natural forest tree trunks, he used units with 10 or more standard trees.
However, when studying for ages before 10, the factors f 1.3 and d 1.3 including bark could not be calculated (because when analyzing the diameter measured at the tree rings, they are diameters without bark). In practice, investigating Acacia mangium forests, usually the values f 1.3 including bark and d 1.3 including bark are meaningful. To solve this problem, the topic establishes the relationship between f 1,3 bark trees and f 13 barkless trees, and the relationship between d 1,3 bark trees and d 1,3 barkless trees, from which f 1,3 and d 1,3 bark trees are deduced for ages before 10. The data to establish these relationships are 16 trees at age 10. In addition, to increase the accuracy of the research results, the topic has inherited the data of 28 analytical trees at Ham Yen Forestry - Tuyen Quang (from age 4 to age 10 - each age has 4 analytical trees). Thus, the total number of trees to establish the relationships of f 1,3 and d 1,3 is 44 trees at ages 4 to 10.
4.1.8.1. Correlation between f 1.3 of barked trees (f 1.3 Cv) and f 1.3 of barkless trees (f 1.3 Kv)
Studies by authors Nguyen Thi Hai Yen (2002), Phan Nguyen Hy (2003) and several other authors have acknowledged that there is a close relationship between f 1.3 Cv and f 1.3 Kv in the form of a straight line: f 1.3 Cv = a + bf 1.3 Kv.
Based on the data of 44 pairs of barked and barkless trees, the study established a correlation between f 1.3 Cv and f 1.3 Kv for Acacia mangium species in the study area. The results calculated on Excel software showed a very high correlation coefficient (R
= 0.922), the regression standard error is small (S y = 0.023), the equation and the regression coefficient b exist (because the probability P(Fr) = 6.31E-19 and P(b) = 6.31E-19 are both less than 0.05), but the coefficient a is very small (a = 0.008417) and does not exist (probability P(a) = 0.79 > 0.05). The equation is adjusted and gives the following correlation results:
f 1.3 Cv = 0.999254.f 1.3 Kv (4.8)





