capital/borrowing capital (14.3%), infected/poor quality seed (14.2%), sedimented/small water level (12.3%) and unquarantined/poorly quarantined shrimp seed source (12.2%).
Table 4.10: Difficulties in raising BTC and TC shrimp in crop 1
Hard
% | |
Shrimp diseases are difficult/impossible to treat. | 20.4 |
Lack of capital/need to borrow capital | 14.3 |
Infected/poor quality seeds | 14.2 |
Sedimented/small level | 12.3 |
No quarantine/little quarantine | 12.2 |
High interest rate | 8.2 |
Polluted/poor quality water | 6.1 |
No direct testing | 4.1 |
Cost increase | 2.0 |
Far from road traffic | 2.0 |
Glowing water | 2.0 |
Algae dieback | 2.0 |
Maybe you are interested!
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Solutions for tourism development in Tien Lang - 10
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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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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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Research on determining varieties and some technical measures to increase productivity and economic efficiency in tomato production in the Red River Delta - 1 -
SWOT Analysis Finds Basic Problems in Farm Economic Development -
Analysis of Technical and Policy Gaps of Project 661 Applied in Hoa Binh Province

4.7.2.6. Analysis of technical and economic factors
Shrimp stocking density tended to decrease from the beginning of January to May, from 18 shrimp/m2 to 15 shrimp/m2 . However, households releasing shrimp in the March group (MV2) had the largest average harvest size (38 shrimp/kg), the shortest average farming time (146 days), and the smallest average FCR of 1.55. The economic efficiency of households releasing shrimp in March was also the highest, with an average profit of 120 million VND/ha and a B/C ratio of 0.82. The number of households with losses accounted for a large proportion.
The lowest was 5.9%. The loss rate in group MV1 was the highest (11.1%). According to the seasonal group, shrimp productivity tended to decrease gradually at the end of the dry season, however, the group released in March (MV2) had the highest profit and B/C ratio and the lowest loss rate.
In terms of pond size, the stocking density of these ponds does not have much difference (from 16-17 fish/m2 ) . However, in the group of ponds with an area < 4,000 m2 ( DT1), the harvest size is the largest (36 fish/kg) and the farming time is the shortest (144 days). The economic efficiency of this group is also the highest compared to the group of ponds ≥
4,000 m 2 and < 5,000 m 2 (DT2) and ≥ 5,000 m 2 (DT3), the average profit is
123 million VND/ha, the average B/C ratio was 0.81 and the number of households with capital loss was 0%. The loss rate of group DT3 was the highest (13.3%). The small pond group (DT1) had the highest profit and B/C ratio, the lowest loss rate.
In terms of density groups, the stocking density group ≥ 15 fish/m 2 and < 20 fish/m 2 (MD2) has the highest economic efficiency with an average profit of 140 million VND.
VND/ha, the average B/C ratio is 0.96. However, group MD2 also has the highest rate of households losing money at 13.3% and the lowest is in the group with stocking density ≥ 20 fish/m 2 (MD3) (7.6%). According to the density group, the higher the density, the higher the productivity, however, in terms of profit, MD2 (average) has the highest profit and the highest B/C ratio compared to the groups with stocking density < 15 fish/m 2 (MD1) and MD2.
Table 4.11: Technical factors according to crop group, stocking density and pond size
Grouping
N=40 | Stocking density (fish/m 2 ) | Survival rate (%) | Harvest size (head/kg) | Time of raising (day) | Productivity (kg/ha) | FCR | |
Season (month) 1 – 2 (MV1) | n 9 | 18 | 58 | 46 | 148 | 2,760 | 1.57 |
3 (MV2) | 17 | 17 | 60 | 38 | 146 | 2,641 | 1.55 |
4-5 (MV3) | 14 | 15 | 60 | 40 | 157 | 2,452 | 1.67 |
Pond size (m 2 ) < 4000 (DT1) | 13 | 17 | 56 | 36 | 144 | 2,722 | 1.69 |
≥ 4000, <5000 (DT2) | 12 | 18 | 63 | 43 | 157 | 2,925 | 1.54 |
≥ 5000 (DT3) | 15 | 16 | 60 | 43 | 150 | 2,239 | 1.56 |
Density (individuals/m 2 ) <15 (MD1) | 12 | 12 | 53.8 | 38 | 160 | 1,496 | 1.73 |
≥ 15, < 20 (MD2) | 15 | 16 | 64.4 | 41 | 146 | 2,740 | 1.37 |
≥ 20 (MD3) | 13 | 22 | 58.9 | 42 | 145 | 3,461 | 1.73 |
Table 4.12: Economic factors by season, stocking density and pond size
Grouping
N=40 | Total fixed costs (million) VND/ha) | Total variable costs (million) VND/ha) | Total cost (million) VND/ha) | Profit (million) VND/ha) | B/C | % loss | |
Season (month) 1 – 2 (MV1) | n 9 | 8.31 | 130.79 | 139.10 | 106.28 | 0.74 | 11.1 |
3 (MV2) | 17 | 9.16 | 123.52 | 132.68 | 120.67 | 0.82 | 5.9 |
4-5 (MV3) | 14 | 8.18 | 123.31 | 131.24 | 101.27 | 0.75 | 7.1 |
Pond size (m 2 ) < 4000 (DT1) | 13 | 11.89 | 136.50 | 148.39 | 123.35 | 0.81 | 0.0 |
≥ 4000, <5000 (DT2) | 12 | 8.64 | 135.96 | 144.60 | 121.35 | 0.75 | 8.3 |
≥ 5000 (DT3) | 15 | 5.79 | 106.26 | 112.05 | 91.06 | 0.77 | 13.3 |
Density (individuals/m 2 ) <15 (MD1) | 12 | 9.08 | 80.06 | 89.14 | 51.32 | 0.59 | 8.3 |
≥ 15, < 20 (MD2) | 15 | 7.71 | 119.98 | 127.69 | 139.79 | 0.96 | 13.3 |
≥ 20 (MD3) | 13 | 9.26 | 172.27 | 181.53 | 131.76 | 0.75 | 7.6 |
4.7.2.7. Correlation analysis of technical and economic factors on productivity
The linear multivariate relationship is presented in Table 4.13. In which density, feed amount, lime cost, chemical cost have positive correlation with shrimp productivity, harvested shrimp size (shrimp/kg) has negative correlation, the number of shrimp/kg increases, shrimp productivity will decrease.
STT | Interpretation | B | Std. Error | t | Sig. | |
1 | Constant | 15,739 | 407,972 | 1,754 | 0.088 | |
2 | Density (individuals/m 2 ) | 17,458 | 29,450 | 0.593 | 0.557 | |
3 | Harvest size (head/kg) | -8,491 | 4,814 | -1,764 | 0.087 | |
4 | Feed amount (kg/ha) | 0.322 | 0.067 | 4,807 | 0.000 | |
5 | Lime cost (VND/ha/crop) | 0.0000354 | 0.0000151 | 2,347 | 0.025 | |
6 | Chemical cost (VND/ha/crop) | 0.0000214 | 0.0000067 | 3,171 | 0.003 | |
Dependent variable: yield (kg/ha) |
Table 4.13: Correlation between factors and productivity of BTC + TC model crop 1
R = 0.905; R 2 = 0.820; Adjusted R 2 = 0.793; sig. F = 0.000
Linear correlation function between productivity and factors:
Y = 15.739+17.458X 1 -8.491X 2 +0.322X 3 +0.0000354X 4 +0.0000214X 5
In there
Y: Productivity (kg/ha/crop) X 1 : Stocking density (fish/m 2 ) X 2 : Harvest size (fish/kg) X 3 : Feed amount (kg/ha)
X 4 : Lime cost (VND/ha/crop)
X 5 : Chemical cost (VND/ha/crop)
4.7.3. Semi-intensive and intensive shrimp farming in crop 2 (BTC + TC crop 2)
4.7.3.1. General information
The survey results of 40 farming households in Vinh Chau and My Xuyen districts show that the farming season is from May to the end of December. The land used to build shrimp ponds was previously used by people for rice production. Shrimp farmers in the second crop have experience in shrimp farming from 3-15 years, on average 7 years. The majority of households have 6 years or more of shrimp farming experience, 72.5%, less than 6 years, 27.5%. The technical level of farmers is from practical experience, 75%, training is 25%. Information sources are regularly collected by farmers from direct extension work such as training, seminars, 37.5%, television stations, 25% and from neighboring farming households, companies selling feed, medicine and chemicals.
4.7.3.2. Technical aspects
The number of households applying the process of raising shrimp without changing water is 42.5%, farmers only add fresh water to the pond to regulate salinity when water evaporates and compensate for the leaked water. The number of households applying the form of changing water is 57.5%, with the amount of water changed monthly from 10-30%/month and an average of 21%/month.
The average total pond surface area is 8,345 m 2 /household. The number of shrimp ponds ranges from 1-5 ponds /household, with an average of 2 ponds /household. The average pond area is 3,615 m 2 /pond. The average pond depth is 1.1 m. The average settling pond area is 1,553 m 2 /household. The number of households without settling ponds accounts for 2.5%. Among the households with settling ponds, the ratio of settling pond area to the area of the shrimp pond is the highest, less than 20%, accounting for 50%, from 20% to less than 30% accounting for 32.5% and greater than 30% accounting for 17.5%. Settling ponds are mainly used for water treatment and storing saltwater used in the process of adding and changing water for shrimp ponds.
The number of farmers applying the wet method of renovation is 55%, and the number of farmers applying the dry method is 45%. Shrimp ponds are drained and dried before starting to renovate the pond. After drying the bottom, the humus and waste from the previous crop are removed from the pond by bulldozer for dry renovation, or scraped and pumped out of the pond by machine (wet renovation) and limed and washed 2-3 times before taking water into the pond to treat and kill weeds and add fertilizer to create water color. The majority of farmers (70%) only use pumps to pump water into the pond and 30% of households also take water in through the tide and combine it with the use of pumps. The quality of water taken into the pond at the beginning of the farming season had an average pH of 8.0 (ranging from 7.0–8.6), average alkalinity of 104 mg/L (ranging from 80–120 mg/L) and average salinity of 5‰ (ranging from 2–10‰).
After processing and coloring the water, the seed can be released. The origin of the seed is purchased directly from the hatchery in Ca Mau by 15%, directly from the hatchery in the Central region by 2.5% and farmers buy seed through agents in the province (mainly from the Central region) by 82.5%. The size of the seed released ranges from PL 12-16 . Research results show that 45% of farmers bring shrimp seed samples for disease testing by PCR method, the remaining 55% of households only know that the shrimp seed has been tested and the quality of the shrimp seed is assessed by sensory, salinity shock and formalin.
The average stocking density was 17 shrimp/m 2 , higher than the study of Tran Van Viet (2006) of 13.2 shrimp/m 2 (from 7-32 shrimp/m 2 ). The average survival rate was 43% (from 6-90%) also higher than the study of Tran Van Viet (2006) of 27.1%. The size of harvested shrimp was 30-150 shrimp/kg, with an average of 51 shrimp/kg. Industrial feed was used to feed the shrimp.
The average farming time is 131 days/crop. The average shrimp yield is 1,828 kg/ha, ranging from 50 - 6,200 kg/ha. The average FCR is 2.2 (Table 4.14). Farmers harvest completely at once by pulling the electric net at 52.5%, draining is 17.5%, and combining both methods is 30%.
The average farming time in the second crop (131 days) is shorter than the first crop (150 days) because many households harvest early due to shrimp disease, and shrimp prices are often high. This shows that the average harvest size of the second crop (51 shrimp/kg) is smaller than the first crop (41 shrimp/kg) as well as the rate of households losing money in the second crop is higher than the first crop.
Table 4.14: Technical factors of the BTC + TC shrimp farming model for crop 2
Interpretation
Medium | Smallest | Biggest | |
Total pond area (m 2 /household) | 8,345 | 4,000 | 20,000 |
Pond area (m 2 /pond) | 3,615 | 2,000 | 6,667 |
Pond water depth (m) | 1.1 | 0.9 | 1.3 |
Settling pond area (m 2 /household) | 1,553 | 500 | 7,000 |
Stocking density (fish/m 2 ) | 17 | 7 | 32 |
Stocking size (PL) | 12 | 16 | |
Rearing time (days) | 131 | 60 | 180 |
Harvest size (head/kg) | 51 | 30 | 150 |
Survival rate (%) | 43 | 6 | 90 |
Food price (VND/kg) | 20,250 | 17,000 | 22,000 |
Yield (kg/ha) | 1,828 | 50 | 6,200 |
FCR | 2.2 | 0.7 | 15 |
4.7.3.3. Economic aspects
Industrial feed is used with feed prices ranging from 17,000–
22,000 VND/kg, average 20,250 VND/kg. Immediately after harvest, 10% of farming households sell raw shrimp directly to processing companies, and 90% sell to warehouse owners.
The average selling price of commercial shrimp was 86,750 VND/kg. The average total cost was 97.92 million VND/ha. The average revenue was 161.37 million VND/ha. The average profit was 75.5 million VND/ha, ranging from a loss of 81 million VND/ha to a profit of 454.86 million VND/ha. The number of households with losses was 35%, the average B/C ratio was 0.6, ranging from a loss of 0.9 to a profit of 2.8 (Table 4.15).
The number of households losing money in shrimp farming in the second crop is 35%, lower than the study of Tran Van Viet (2006) of 64%. Comparing the average rate of shrimp farming households losing money in the first and second crop is 21.5%, lower than the years 2002 which was 25 - 30% (Le Xuan Sinh, 2003), 56.2% in 2005 (Tran Van Viet, 2006). The rate of losing money tends to decrease. In general. The profit in the first crop (110.64 million VND/ha/crop) is higher than that in the second crop (75.5 million VND/ha/crop), the reason is that the number of losing households is higher.
Operating capital: The number of households that did not borrow operating capital accounted for 50%, lower than in crop 1. The level of borrowing operating capital was also higher in crop 1, more than 95.0% borrowed more than 50.0% of operating capital (Figure 4.15).
Table 4.15: Loan level of BTC+TC shrimp farmers in crop 2
Interpretation
% | % loan level | |
Percentage of households without loans | 50 | |
Percentage of households with loans | 50 | |
Borrow from 75-100% of operating capital | 55.0 | |
Borrow from 50-74% of operating capital | 40.0 | |
Borrow from < 49% of working capital | 5.0 |
The average cost of commercial shrimp produced from this model is 53,566 VND/kg. Variable costs account for the majority of the cost of shrimp farming at 89.8%, fixed costs account for 10.2%. Of which, feed costs are the highest at 55.0%, followed by chemical costs at 10.4% and seed costs at 7.0%. Comparing the cost of commercial shrimp, the cost of shrimp in crop 2 (53,566 VND/kg) is higher than in crop 1 (51,245 VND/kg). In the cost structure, feed costs account for 57.2%, higher than in crop 2 (55.0%) because in crop 2 the proportion of other costs such as seed, fixed costs, fuel, and dredging increases.
Table 4.16: Economic factors of the BTC + TC shrimp farming model crop 2
Unit: million VND/ha/crop
Interpretation
Medium | Smallest | Biggest | ||
Fixed costs | 9.99 | |||
Pond depreciation | 0.96 | 0.38 | 2.15 | |
Pump depreciation | 2.07 | 0.6 | 7.02 | |
Fan blade depreciation | 9.96 | 1.64 | 15.87 | |
Variable costs | 87.93 | |||
Food | 54.74 | 2.2 | 202.38 | |
Slug, dredge | 5.83 | 1.75 | 15 | |
Breeding stock | 6.82 | 1.79 | 15.87 | |
Lime | 4.16 | 0.88 | 10 | |
Chemical | 10.23 | 1 | 49 | |
Fuel | 4.79 | 0.3 | 13.46 | |
Other | 1.61 | 0 | 13.85 | |
Total cost | 97.92 | 18.58 | 289.14 | |
Selling price (VND) | 86.75 | 20,000 | 125,000 | |
Cost price (VND) | 53,566 | |||
Total revenue | 161.37 | 1 | 744 | |
Total profit | 75.5 | -81 | 454.86 | |
B/C | 0.6 | -0.9 | 2.8 | |
Note: B: Total profit, C: Total cost | ||||
10.4
4.2
7.0
5.9
4.9 1.6
10.2
Fixed Cost Food
Slug, Slug, Lime Seed
Fuel Chemicals
Other
55.0
Figure 4.35: Cost structure of commercial shrimp price (BTC + TC crop 2)
4.7.3.4. Shrimp diseases
The survey results showed that the number of shrimp farming households with completely healthy shrimp ponds accounted for 26.5%, higher than in crop 1 (20.0%). In general, when compared with crop 1, the percentage of diseases that appeared was not much different. The rate of white spot disease (14.3%) and yellow head disease (8.2%) was higher than in crop 1, possibly because the water environment fluctuated more, so shrimp were more susceptible to disease outbreaks, and shrimp had less algae than in crop 1. The time of disease appearance in ponds in crop 2 (30 days) was later than in crop 1 (20 days) (Table 4.17).
Table 4.17: Diseases occurring in ponds
TT
Type of disease | Rate of ponds affected sick (%) | Time of departure present (day of raising) | Note | |
1 | White spot syndrome virus (WSSV) | 14.3 | 30-75 | 45-75 days at most |
2 | Shrimp is occupied by algae | 8.2 | 45-120 | |
3 | Black carry | 8.2 | 60-120 | |
4 | Tailed caterpillar | 8.2 | 60-120 | |
5 | Red body of unknown cause | 8.2 | 30 | |
6 | Golden Head (YHV) | 8.2 | 60 | |
7 | Rickets (MBV) | 6.1 | 60 | |
8 | Death of unknown cause | 6.1 | Scattered | |
9 | White manure | 4.1 | 30-60 | |
10 | Soft shell | 2 | 90 |
4.7.3.5. Difficulties
The five reasons that shrimp farmers believe are causing difficulties for shrimp farming today are difficult/impossible to treat shrimp diseases (23.0%), unquarantined/less tested shrimp seed sources (18.9%), high interest rates on external loans (14.9%), polluted/poor quality water sources (12.2%), and lack of technical information (6.8%).
Table 4.18: Difficulties of BTC + TC shrimp farming in crop 2
Hard
% | |
Shrimp diseases are difficult/impossible to treat. | 23.0 |
No quarantine/little testing | 18.9 |
High interest rate | 14.9 |
Polluted water source/poor quality water | 13.5 |
Lack of information, technique | 6.8 |
No direct testing | 5.4 |
Small/silted canal | 4.1 |
Need to borrow/lack of capital | 5.4 |
Poor quality seed | 4.1 |
High price breed | 1.4 |
Far from road traffic | 1.4 |
Algae dieback | 1.4 |
4.7.3.6. Analysis of technical and economic factors
Grouping by season, we see that seed release in August (MV5) has the highest average yield (1,829 kg/ha/crop), the highest average profit (79.679 million VND/ha/crop), however, the B/C ratio is average (0.4) and the loss rate is average (43%) compared to the 2 groups of seed release from June to July (MV4) and from September to November (MV6). The MV4 group has the lowest average yield (1,461 kg/ha/crop), the lowest average profit (38.872 million VND/ha/crop) compared to the MV5 and MV6 groups, and the highest rate of households losing money. The MV4 group has the lowest average shrimp stocking density.
the most (14 birds/m2 ) .
Classification by pond size group: results show that the area group ≥ 3,000 m 2 /pond and
≤ 4,000 m 2 /pond (DT5) has an average stocking density of 17 fish/m 2, reaching the average density compared to the area group < 3,000 m 2 /pond (DT4) and the group ≥ 4,000 m 2 /pond (DT6), but has the highest average yield (1,967 kg / ha / crop), the highest average profit (91,681 million VND / ha / crop), the highest average B/C ratio (0.7) and the lowest loss rate (14%). According to the pond size group, the smaller the pond area, the higher the stocking density (DT4, 19 fish/m 2 ; DT5, 17 fish/m 2 ; DT6, 15 fish/m 2 ).
By density group: the higher the stocking density, the higher the yield, the higher the profit, but the B/C ratio decreases, the rate of households with losses tends to increase. The stocking density group ≥20 PL/m 2 (MD6) has the highest average yield (2,291 kg/ha/crop), the highest profit (96.725 million VND/ha/crop), but the average B/C ratio (0.4) is lower than the stocking group <15 PL/m 2 (MD4) (0.5), the rate of households with losses is at an average level (36%). The group with the lowest density MD4 has the lowest profit (45.228 million VND/ha/crop), but has the highest B/C ratio (0.5) and the lowest rate of households with losses (31%).





