ເຕັກໂນໂລຢີ

Community supported pasture and rangeland rehabilitation works [ແອນໂກລາ]

technologies_3141 - ແອນໂກລາ

ຄວາມສົມບູນ: 88%

1. ຂໍ້​ມູນ​ທົ່ວ​ໄປ

1.2 ຂໍ້ມູນ ການຕິດຕໍ່ພົວພັນ ຂອງບຸກຄົນທີ່ສໍາຄັນ ແລະ ສະຖາບັນ ທີ່ມີສ່ວນຮ່ວມ ໃນການປະເມີນເອກກະສານ ເຕັກໂນໂລຢີ

ບັນດາຜູ້ຕອບແບບສອບຖາມທີ່ສໍາຄັນ ()

ຜຸ້ຊ່ຽວຊານ ດ້ານການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:
ຜຸ້ຊ່ຽວຊານ ດ້ານການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:
ຊື່ໂຄງການ ທີ່ອໍານວຍຄວາມສະດວກ ໃນການສ້າງເອກກະສານ/ປະເມີນ ເຕັກໂນໂລຢີ (ຖ້າກ່ຽວຂ້ອງ)
Reabilitação de terras e gestão das áreas de pastagem nos sistemas de produção agro-pastoris dos pequenos produtores no sudoeste de Angola (RETESA)
ຊື່ສະຖາບັນ (ຫຼາຍສະຖາບັນ) ທີ່ອໍານວຍຄວາມສະດວກ ໃນການສ້າງເອກກະສານ / ປະເມີນ ເຕັກໂນໂລຢີ (ຖ້າກ່ຽວຂ້ອງ)
Food and Agriculture Organisation Angola (FAO) - ແອນໂກລາ

1.3 ເງື່ອນໄຂ ກ່ຽວກັບ ການນໍາໃຊ້ຂໍ້ມູນເອກະສານ ທີ່ສ້າງຂື້ນ ໂດຍຜ່ານ ອົງການພາບລວມຂອງໂລກ ທາງດ້ານແນວທາງ ແລະ ເຕັກໂນໂລຢີ ຂອງການອານຸລັກ ທໍາມະຊາດ (WOCAT)

ຜູ້ປ້ອນຂໍ້ມູນ ແລະ ບຸກຄົນສຳຄັນ ທີ່ໃຫ້ຂໍ້ມູນ (ຫຼາຍ) ຍິນຍອມ ຕາມເງື່ອນໄຂ ໃນການນຳໃຊ້ຂໍ້ມູນ ເພື່ອສ້າງເປັນເອກກະສານຂອງ WOCAT:

ແມ່ນ

1.4 ແຈ້ງການວ່າ ດ້ວຍຄວາມຍືນຍົງຂອງ ເຕັກໂນໂລຢີ

ການນໍາໃຊ້ ເຕັກໂນໂລຢີ ດັ່ງກ່າວໄດ້ອະທິບາຍ ເຖິງບັນຫາ ກ່ຽວກັບ ການເຊື່ອມໂຊມຂອງດິນບໍ? ຖ້າບໍ່ດັ່ງນັ້ນ ມັນບໍ່ສາມາດ ຢັ້ງຢືນໄດ້ວ່າ ເປັນເຕັກໂນໂລຊີ ໃນການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ? :

ບໍ່ແມ່ນ

2. ການອະທິບາຍ ເຕັກໂນໂລຢີ ຂອງການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ

2.1 ຄໍາອະທິບາຍສັ້ນຂອງ ເຕັກໂນໂລຢີ

ຄໍານິຍາມ ຂອງເຕັກໂນໂລຢີ:

Rehabilitation of rangelands involves selection of key pasture and fodder species, and their reintroduction into strategic areas through stakeholder participation. The technology is also supported by communal management plans, which were created to address the root causes of land degradation.

2.2 ການອະທິບາຍ ລາຍລະອຽດ ຂອງເຕັກໂນໂລຢີ

ການພັນລະນາ:

This technology was developed and implemented through the RETESA Project “Land rehabilitation and rangelands management in smallholder agropastoral production systems in south-western Angola”. RETESA is a project owned and implemented by the Ministry of Environment of the Government of Angola, with technical and methodological assistance from The Food and Agriculture Organization of the United Nations (FAO), and financed by the Global Environment Facility (GEF).
Inappropriate grazing regimes and poor livestock management by pastoral communities in SW Angola have led to degradation of rangeland and pastoral resources, with perennial grassland species and shrubs having been effectively eliminated. This is despite the fact that the pastoral communities of the area know their environment extremely well and are aware of the land degradation happening around them. Under the project they identified crucial areas for rehabilitation works, selecting mostly areas around water points that have been in use both by local and transhumant herders. Through these works, the local community sought to (a) increase ground cover to reduce sediment loads entering waterways (erosion control), (b) provide shade for livestock, (c) increase forage production and (d) introduce legumes and multipurpose forage trees in areas of high animal traffic. A total of four areas in the Bibala and Virei Municipalities were identified for the activities.
The communities were closely involved in the selection and propagation of plant species for the rehabilitation works. The project field staff also ran field palatability trials with them to confirm that the plants selected met their expectations. These participatory trials were also aimed at enhancing their understanding of livestock nutrition and how it related to animal health. Once the species were chosen, seed was collected by the communities and the Project Technicians, and was multiplied in 32 Agro-Pastoral Field School Nurseries and 2 Government funded Veterinary Research Stations. A total of 15 species were identified, with the grasses Eragrostis superba, Urochloa mosambicensis, and the trees Acacia nilotica, Faidherbia albida, Leucaena leucocephala and Moringa oleifera being the most valued by the communities as forage and multipurpose species. The trees were germinated from seed with success. However, native grass species failed to germinate by standard methods - early field trials having ruled out direct seeding methods. Thus they were multiplied by root division of plants collected from cultivated fields. This avoided removal of grass from natural areas.
As the majority of the areas selected for the rehabilitation works were focused around water points and waterways, the soils were generally alluvial, sandy loams. Precipitation is highest in the areas to the north: it ranges from 600 mm in the upper areas of the Bibala Municipality to 200 mm in the areas to the south in Virei. In general, the vegetation communities could be described as dry sclerophyll woodlands with Colophospermum mopane being the dominant tree species, with forest cover decreasing in height and density as one moves south toward drier areas.
Through close collaboration with the participant communities, three rehabilitation methods were designed and improved upon throughout the Project's duration. Method 1 was used to plant open areas within the rehabilitation zone, Method 2 was employed to introduce and protect concentrated plantings of the selected species in strategic locations within the landscape, and Method 3 was preferred for the recuperation of riparian vegetation and to reduce sediment loads in waterways. The three methods used are described in more detail in the Technical Drawings. To increase the sense of ownership and thus the sustained effectiveness of the rehabilitation works, land management plans and other supporting activities were also carried out.

2.3 ຮູບພາບຂອງເຕັກໂນໂລຢີ

2.5 ປະເທດ / ເຂດ / ສະຖານທີ່ບ່ອນທີ່ ເຕັກໂນໂລຢີ ໄດ້ຮັບການນໍາໃຊ້ ແລະ ທີ່ຖືກປົກຄຸມດ້ວຍການປະເມີນຜົນ

ປະເທດ:

ແອນໂກລາ

ພາກພື້ນ / ລັດ / ແຂວງ:

Province of Namibe

ຂໍ້ມູນເພີ່ມເຕີມຂອງສະຖານທີ່:

Municipalities of Bibala and Virei

ໃຫ້ລະບຸ ການແຜ່ຂະຫຍາຍ ເຕັກໂນໂລຢີ:
  • ນໍາໃຊ້ໃນຈຸດສະເພາະ / ແນໃສ່ນໍາໃຊ້ໃນພື້ນທີ່ຂະໜາດນ້ອຍ
ຄວາມຄິດເຫັນ:

There are 3 main rehabilitation areas, all within the Namibe Province in Southern Angola.
Planting areas are selected due to their importance and relevance to the local communities. For the most part, the plantings have been centred around key water points. In order to increase impact and scale up the process of rangeland rehabilitation and improvement, management plans are negotiated and agreed upon by the communities through the Green Negotiated Territorial Development Approach (GreeNTD) processes.

2.6 ວັນທີໃນການຈັດຕັ້ງປະຕິບັດ

ຖ້າຫາກວ່າ ບໍ່ຮູ້ຈັກ ປີທີ່ຊັດເຈນ ແມ່ນໃຫ້ປະມານ ວັນທີເອົາ:
  • ຕໍ່າກວ່າ 10 ປີ ຜ່ານມາ (ມາເຖິງປະຈຸບັນ)

2.7 ການນໍາສະເໜີ ເຕັກໂນໂລຢີ

ໃຫ້ລະບຸ ເຕັກໂນໂລຢີ ໄດ້ຖືກຈັດຕັ້ງປະຕິບັດຄືແນວໃດ?
  • ໂດຍຜ່ານໂຄງການ / ການຊ່ວຍເຫຼືອຈາກພາຍນອກ
ຄວາມຄິດເຫັນ (ປະເພດ ໂຄງການ ແລະ ອື່ນໆ):

The proposed project: “Land rehabilitation and rangelands management in smallholders’ agropastoral production systems in southwestern Angola” (RETESA) is a joint effort by the Ministério do Ambiente (MA), Ministério da Agricultura e do Desenvolvimento Rural e das Pescas (MINANDER), Governo Provincial do Namibe, Governo Provincial do Huila, and Governo Provincial de Benguela, together with FAO and GEF. In line with the GEF-5 Land Degradation strategy, the project’s goal is to create an enhanced enabling environment in the agricultural sector and a sustained flow of agro-ecosystem services.

3. ການໃຈ້ແຍກ ເຕັກໂນໂລຢີ ໃນການຄຸ້ມຄອງ ດິນແບບຍືນຍົງ

3.1 ຈຸດປະສົງຫຼັກ (ຫຼາຍ) ຂອງເຕັກໂນໂລຢີ

  • ປັບປຸງ ການຜະລິດ
  • ຫຼຸດຜ່ອນ, ປ້ອງກັນ, ຟື້ນຟູ ການເຊື່ອມໂຊມຂອງດິນ
  • ການອະນຸລັກ ລະບົບນິເວດ
  • ປົກປັກຮັກສາ / ການປັບປຸງຊີວະນາໆພັນ
  • ຫຼຸດຜ່ອນຄວາມສ່ຽງ ທາງໄພພິບັດທໍາມະຊາດ
  • ປັບຕົວຕໍ່ກັບການປ່ຽນແປງດິນຟ້າອາກາດ / ທີ່ຮ້າຍແຮງ ແລະ ຜົນກະທົບ
  • ຫຼຸດຜ່ອນຜົນກະທົບ ຈາກການປ່ຽນແປງດິນຟ້າອາກາດ
  • ສ້າງຜົນກະທົບ ທາງເສດຖະກິດ ທີ່ເປັນປະໂຫຍດ

3.2 ປະເພດການນໍາໃຊ້ທີ່ດິນ ໃນປະຈຸບັນ() ທີ່ເຕັກໂນໂລຢີ ໄດ້ຖືກນໍາໃຊ້

ທົ່ງຫຍ້າລ້ຽງສັດ

ທົ່ງຫຍ້າລ້ຽງສັດ

ການລ້ຽງສັດແບບປ່ອຍ ຕາມທຳມະຊາດ:
  • ການລ້ຽງສັດແບບເຄີ່ງປ່ອຍ
  • Transhumance movements
Animal type:
  • cattle - dairy
  • cattle - non-dairy beef
  • goats
Products and services:
  • meat
  • milk
ທິດທາງໄຫຼຂອງນໍ້າ, ນໍ້າ,​ ດິນທາມ

ທິດທາງໄຫຼຂອງນໍ້າ, ນໍ້າ,​ ດິນທາມ

  • ທໍ່ລະບາຍນໍ້າ, ທິດທາງນໍ້າ
  • ໜອງ, ເຂື່ອນໄຟຟ້າ
  • Natural springs
ຄວາມຄິດເຫັນ:

Number of growing seasons per year: 1
Livestock density: Official data is not available and true livestock numbers are unknown.

3.3 Has land use changed due to the implementation of the Technology?

Has land use changed due to the implementation of the Technology?
  • Yes (Please fill out the questions below with regard to the land use before implementation of the Technology)
ຄວາມຄິດເຫັນ:

Crop land is increasing in the area as population increases and people move towards more sedimentary livelihoods.

3.4 ການສະໜອງນ້ຳ

ການສະໜອງນໍ້າ ໃນພື້ນທີ່ ທີ່ໄດ້ນໍາໃຊ້ ເຕັກໂນໂລຢີ:
  • ນໍ້າຝົນ

3.5 ການນໍາໃຊ້ເຕັກໂນໂລຢີ ທີ່ຢູ່ໃນກຸ່ມການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ

  • ການຄຸ້ມຄອງສັດລ້ຽງ ແລະ ທົ່ງຫຍ້າລ້ຽງສັດ
  • ການປັບປຸງດິນ / ພືດຄຸມດິນ

3.6 ມາດຕະການ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ ປະກອບດ້ວຍ ເຕັກໂນໂລຢີ

ມາດຕະການ ທາງດ້ານພືດພັນ

ມາດຕະການ ທາງດ້ານພືດພັນ

  • V1: ເປັນໄມ້ຢືນຕົ້ນ ແລະ ການປົກຫຸ້ມຂອງໄມ້ພຸ່ມ
  • V2: ຫຍ້າ ແລະ ພືດສະໝູນໄພທີ່ເປັນໄມ້ຢືນຕົ້ນ
ມາດຕະການ ທາງດ້ານການຄຸ້ມຄອງ

ມາດຕະການ ທາງດ້ານການຄຸ້ມຄອງ

  • M2: ການປ່ຽນແປງ ການຈັດການຄຸ້ມຄອງ / ລະດັບຄວາມໜາແໜ້ນ
ຄວາມຄິດເຫັນ:

The management plans created at the community and administrative level identify a number of large areas which are to serve as 'Grazing Reverses' for the dry season. Therefore, the agreements call for all livestock to abandon the area at the onset of the first rains and not return until the Pastoral Management Forum agrees to open the area for grazing. Once open, the range is available to all pastoralists, those that live in the immediate area and those moving through on their transhumance migration.

3.7 ປະເພດດິນເຊື່ອມໂຊມ ຫຼັກທີ່ໄດ້ນໍາໃຊ້ ເຕັກໂນໂລຢີ

ດິນເຊາະເຈື່ອນ ໂດຍນໍ້າ

ດິນເຊາະເຈື່ອນ ໂດຍນໍ້າ

  • Wt: ການສູນເສຍຊັ້ນໜ້າດິນ / ການເຊາະເຈື່ອນຜິວໜ້າດິນ
  • Wr: ແຄມຕາຝັ່ງເຈື່ອນ
ການເຊື່ອມໂຊມ ທາງຊີວະພາບ

ການເຊື່ອມໂຊມ ທາງຊີວະພາບ

  • Bc: ການຫຼຸດຜ່ອນການປົກຫຸ້ມຂອງພືດ
  • Bh: ການສູນເສຍ ທີ່ຢູ່ອາໃສ ຂອງສິ່ງທີ່ມີຊິວິດ
  • Bq: ປະລິມານ / ອິນຊີວັດຖຸຫຼຸດລົງ
  • Bs: ຄຸນນະພາບ / ການອັດແໜ້ນ ຂອງສາຍພັນຫຼຸດລົງ
  • Bl: ການສູນເສຍ ຈຸລິນຊີໃນດິນ

3.8 ການປ້ອງກັນ, ການຫຼຸດຜ່ອນ, ຫຼືການຟື້ນຟູຂອງການເຊື່ອມໂຊມຂອງດິນ

ໃຫ້ລະບຸ ເປົ້າໝາຍ ເຕັກໂນໂລຢີ ທີ່ພົວພັນ ກັບຄວາມເຊື່ອມໂຊມຂອງດິນ:
  • ຫຼຸດຜ່ອນການເຊື່ອມໂຊມຂອງດິນ
  • ການຟື້ນຟູ / ຟື້ນຟູດິນທີ່ຊຸດໂຊມ

4. ຂໍ້ກໍາໜົດ, ກິດຈະກໍາການປະຕິບັດ, ວັດຖຸດິບ, ແລະຄ່າໃຊ້ຈ່າຍ

4.1 ເຕັກນິກ ໃນການແຕ້ມແຜນວາດ ເຕັກໂນໂລຢີ

ຄຸນລັກສະນະ ຂອງເຕັກນິກ (ທີ່ກ່ຽວຂ້ອງ ກັບການແຕ້ມແຜນວາດ ທາງດ້ານເຕັກນີກ):

Planting is typically based on three different methods, as seen in the figure above.
- Method 1 relies on placing a leguminous, multipurpose tree species in the ground with two native grass species to each side of the tree. The holes are dug and a small amount of manure is placed in the bottom of the hole, adding some water if it is readily available. Then the trees and grasses are planted and well-watered. Finally, a branch or two of thorny shrubs or trees are placed over the plants to protect them from being grazed (where possible, dead branches should be used, rather than cutting living plants).
- Method 2 requires the creation of an enclosed, protected area which is then planted at high densities, preferably in low-lying areas where adequate soil moisture is available. Dry, dead branches from thorny trees and shrubs are used to create the enclosures and provide protection to these plantings.
- Method 3 is based on the creation of a 'leaky weir', which is a small stone barrier, horizontal to the flow of water (on the contour) planted with a mixture of native riparian species. This is intended to slow the flow of water and stimulate the recovery of riparian vegetation. The plants are also protected with dry, dead branches from thorny trees and shrubs in this method.
To increase their effectiveness, it is recommended that the three methods be combined within the landscape, as seen in the 4th slide 'Field application of methods'.

ຜູ້ຂຽນ:

Projecto RETESA

ວັນທີ:

10/01/2018

4.2 ຂໍ້ມູນທົ່ວໄປກ່ຽວກັບການຄິດໄລ່ປັດໃຈຂາເຂົ້າໃນການຜະລິດ ແລະ ມູນຄ່າອື່ນໆ

ລະບຸ ວິທີການ ຄຳໃຊ້ຈ່າຍ ແລະ ປັດໄຈນໍາເຂົ້າ ທີ່ໄດ້ຄິດໄລ່:
  • ຕໍ່ຫົວໜ່ວຍ ທີ່ໄດ້ຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ
ໃຫ້ລະບຸຫົວໜ່ວຍ:

3345 seedlings produced, delivered and planted

ກໍານົດຂະຫນາດຂອງຫົວນ໋ວຍ (ຖ້າກ່ຽວຂ້ອງ):

3345 units

ລະບຸ ສະກຸນເງິນທີ່ໃຊ້ສໍາລັບ ການຄິດໄລ່ຄ່າໃຊ້ຈ່າຍ:
  • USA
ລະບຸ ຄ່າຈ້າງ ຄ່າແຮງງານສະເລ່ຍ ຕໍ່ ວັນ:

6 Dollars

4.3 ການສ້າງຕັ້ງກິດຈະກໍາ

ກິດຈະກໍາ Timing (season)
1. Meetings and field visits with participant communities to identify plant species and their uses Best during growing season
2. Further meetings to decide on which species are to be multiplied and arrange seed collection Near end of growing season
3. Seed collection and transportation When seed is available (varies with species)
4. Instalation of irrigation systems Most communiites need a water extraction and distribution system to create nurseries
5. Delivery of nursery supplies and instalation of shade cloth Nurseries should have water access and shade
6. Planting of seeds and care for seedlings at nursery Formed part of Agro-Pastoral Farmer Field School activities
7. Identification of planting areas and timing Should be at beginning of rainy season, or when soil moisture permits
8. Organisation of materials and tools At least 1 week before the planting
9. Planting day (preparation of planting holes and transplanting of seedlings) 2 days maximum was seen to be optimal
10. Watering until the plants are established Usually a maximum of 3 watering over 1 week after the plantings
11. Follow up visits to make sure management agreements are being respected and plants are not being eaten by stock until they are ready Plants should not be grazed for at least 6 months from planting time until they are well established
ຄວາມຄິດເຫັນ:

The activities and costs given were those needed to produce and plant 3,345 trees and grasses in the 4 rehabilitation areas. Given that 3,345 plants were produced at a cost of $3284.75, the cost per plant produced and planted in the field is $0.98. Seedlings available through local, government nurseries were $2.00 per unit, but only exotic ornamentals were available. However, it can be expected that in other contexts and locations, it would be cheaper to buy seedlings, instead of training communities and creating numerous small-scale nurseries, though clearly these communities will not ‘own’ the process as well as if they were involved from the beginning.

4.4 ຕົ້ນທຶນ ແລະ ປັດໄຈຂາເຂົ້າທີ່ຈໍາເປັນໃນຈັດຕັ້ງປະຕິບັດ

ລະບຸ ປັດໃຈ ນໍາເຂົ້າ ໃນການຜະລີດ ຫົວໜ່ວຍ ປະລິມານ ຕົ້ນທຶນ ຕໍ່ຫົວໜ່ວຍ ຕົ້ນທຶນທັງໝົດ ຂອງປັດໃຈຂາເຂົ້າ ໃນການຜະລິດ % ຂອງຕົ້ນທຶນທັງໝົດ ທີ່ຜູ້ນໍາໃຊ້ທີ່ດິນ ໃຊ້ຈ່າຍເອງ
ແຮງງານ Project Technicians/Drivers/Consultants, etc Person-days 30.0 20.0 600.0
ແຮງງານ Plant identification activities and seed collection Person-days 10.0 6.0 60.0 100.0
ແຮງງານ Plant nursery creation and plant production Person-days 16.0 6.0 96.0 100.0
ແຮງງານ Participation during planting days Person-days 25.0 10.0 250.0 90.0
ອຸປະກອນ Vehicle Trips 10.0 40.0 400.0
ອຸປະກອນ Nursery supplies (including water system which also supplies water to Farmer Field School) Materials 1.0 800.0 800.0 10.0
ອຸປະກອນ Planting supplies (shovels, hoes, wheelbarrows, etc.) Materials 1.0 120.0 120.0
ອຸປະກອນ Other improvements to water point (fencing, cement blocks, cement, hoses, etc.) Materials 1.0 250.0 250.0
ອຸປະກອນ Maps (traced onto paper from projected images for management purposes) Materials 1.0 10.0 10.0
ອຸປະກອນ Food and Refreshments Per person 25.0 2.5 62.5
ຝຸ່ນ ແລະ ຢາຊີວະພາບ Manure (50 grams per sack, 12.500 sacks) Kilos 625.0 0.25 156.25 100.0
ວັດສະດຸກໍ່ສ້າງ Shade-cloth m2 320.0 1.5 480.0
ຕົ້ນທຶນທັງໝົດ ໃນການຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ 3284.75
Total costs for establishment of the Technology in USD 3284.75
ຖ້າຫາກຜູ້ນຳໃຊ້ທີ່ດິນ ນຳໃຊ້ມູນຄ່າຕ່ຳກວ່າ 100% ໃຫ້ລະບຸ ແມ່ນໃຜເປັນຜູ້ຊ່ວຍ ໃນລາຍຈ່າຍທີ່ເຫຼືອ:

Remaining costs were provided by the RETESA Project.

ຄວາມຄິດເຫັນ:

Production depends on the ability of the pastoral communities to produce viable plants. If they are unable to do so, then plants can be bought from Government funded nurseries, though costs per plant will most rise though it can substitute the need for having to purchase a water supply system. The total shown here reflects a percentage (16%) of the costs of installing a water system that supplied water to the whole of the Agro-Pastoral Farmer Field School. These systems usually included a 10,000 litre water tank, a gasoline water pump, extraction pipe and parts, 100 to 200 mts of 1.5" hoses and parts and 3 kms of drip irrigation hose.

4.5 ບໍາລຸງຮັກສາ / ແຜນຈັດຕັ້ງປະຕິບັດ ກິດຈະກໍາ

ກິດຈະກໍາ ໄລຍະເວລາ / ຄວາມຖີ່
1. Meetings to ensure management agreements are being respected. Once every 3 to 6 months, especially before and after rainy season.
2. Repairs and replacement of nursery supplies. Once a year.
3. Replanting of dead seedlings Just before and during rainy season.

4.6 ຄ່າໃຊ້ຈ່າຍ ແລະ ປັດໄຈນໍາເຂົ້າທີ່ຈໍາເປັນສໍາລັບການບໍາລຸງຮັກສາກິດຈະກໍາ / ແຜນປະຕິບັດ (ຕໍ່ປີ)

ລະບຸ ປັດໃຈ ນໍາເຂົ້າ ໃນການຜະລີດ ຫົວໜ່ວຍ ປະລິມານ ຕົ້ນທຶນ ຕໍ່ຫົວໜ່ວຍ ຕົ້ນທຶນທັງໝົດ ຂອງປັດໃຈຂາເຂົ້າ ໃນການຜະລິດ % ຂອງຕົ້ນທຶນທັງໝົດ ທີ່ຜູ້ນໍາໃຊ້ທີ່ດິນ ໃຊ້ຈ່າຍເອງ
ແຮງງານ Visits to sites and tour of planting areas. Person-days 4.0 20.0 80.0 50.0
ແຮງງານ Driver. Person-days 1.0 20.0 20.0
ແຮງງານ Replanting of dead seedlings Person-days 2.0 6.0 12.0 100.0
ແຮງງານ Watering Person-days 14.0 6.0 84.0 100.0
ອຸປະກອນ Vehicle Trips 1.0 40.0 40.0
ອຸປະກອນ Watering cans and buckets Materials 4.0 5.0 20.0
ຕົ້ນທຶນທັງໝົດ ທີ່ໃຊ້ໃນການບໍາລຸງຮັກສາ ເຕັກໂນໂລຢີ 256.0
Total costs for maintenance of the Technology in USD 256.0
ຖ້າຫາກຜູ້ນຳໃຊ້ທີ່ດິນ ນຳໃຊ້ມູນຄ່າຕ່ຳກວ່າ 100% ໃຫ້ລະບຸ ແມ່ນໃຜເປັນຜູ້ຊ່ວຍ ໃນລາຍຈ່າຍທີ່ເຫຼືອ:

The RETESA Project provided an important part of both material and technical support to the communities, though the communities also contributed substantially.

4.7 ປັດໄຈ ທີ່ສໍາຄັນ ທີ່ສົ່ງຜົນກະທົບ ຕໍ່ຄ່າໃຊ້ຈ່າຍ

ໃຫ້ອະທິບາຍ ປັດໃຈ ທີ່ສົ່ງຜົນກະທົບ ຕໍ່ຕົ້ນທຶນ ໃນການຈັດຕັ້ງປະຕິບັດ:

The activities and costs given were those needed to produce and plant 3,345 trees and grasses in the 4 rehabilitation areas. Given that 3.345 plants were produced at a cost of $3284.75, the cost per plant produced and planted in the field is $0.98. Seedlings avaliable through local, government nurseries were $2.00 per unit, but only exotic ornamentals were avaliable. However, it can be expected that in other contexts and locations, it would be cheaper to buy seedlings instead of training communities and creating numerous small scale nurseries, though clearly these communities will not appropriate the process as well as if they were involved from the beginning.

5. ສະພາບແວດລ້ອມທໍາມະຊາດ ແລະ ມະນຸດ

5.1 ອາກາດ

ປະລິມານນໍ້າຝົນປະຈໍາປີ
  • < 250 ມີລິແມັດ
  • 251-500 ມີລິແມັດ
  • 501-750 ມີລິແມັດ
  • 751-1,000 ມີລິແມັດ
  • 1,001-1,500 ມີລິແມັດ
  • 1,501-2,000 ມີລິແມັດ
  • 2,001-3,000 ມີລິແມັດ
  • 3,001-4,000 ມີລິແມັດ
  • > 4,000 ມີລິແມັດ
ຂໍ້ມູນສະເພາະ / ຄວາມເຫັນກ່ຽວກັບ ປະລິມານນໍ້າຝົນ:

In the past, the rainy season started in October or November and ran until May. However, the rains in the last few years have fallen in January to April.

ໃຫ້ລະບຸ ຊື່ສະຖານີ ອຸຕຸນິຍົມ ເພື່ອເປັນຂໍ້ມູນອ້າງອີງ:

None in the area.

ເຂດສະພາບອາກາດກະສິກໍາ
  • ເຄິ່ງແຫ້ງແລ້ງ

5.2 ພູມິປະເທດ

ຄ່າສະເລ່ຍ ຄວາມຄ້ອຍຊັນ:
  • ພື້ນທີ່ຮາບພຽງ (0-2%)
  • ອ່ອນ (3-5 %)
  • ປານກາງ (6-10 %)
  • ມ້ວນ (11-15 %)
  • ເນີນ(16-30%)
  • ໍຊັນ (31-60%)
  • ຊັນຫຼາຍ (>60%)
ຮູບແບບຂອງດິນ:
  • ພູພຽງ / ທົ່ງພຽງ
  • ສັນພູ
  • ເປີ້ນພູ
  • ເນີນພູ
  • ຕີນພູ
  • ຮ່ອມພູ
ເຂດລະດັບສູງ:
  • 0-100 ແມັດ a.s.l.
  • 101-500 ແມັດ a.s.l.
  • 501-1,000 ແມັດ a.s.l.
  • 1,001-1,500 ແມັດ a.s.l.
  • 1,501-2,000 ແມັດ a.s.l.
  • 2,001-2,500 ແມັດ a.s.l.
  • 2,501-3,000 ແມັດ a.s.l.
  • 3,001-4,000 ແມັດ a.s.l.
  • > 4,000 ແມັດ a.s.l.
ໃຫ້ລະບຸ ເຕັກໂນໂລຢີ ທີ່ໄດ້ຖືກນຳໃຊ້:
  • ບໍ່ກ່ຽວຂ້ອງ
ຄຳເຫັນ ແລະ ຂໍ້ມູນສະເພາະ ເພີ່ມເຕີມ ກ່ຽວກັບ ພູມີປະເທດ:

Usually the planting are undertaken along river plains and river banks, as they are the only areas that have the necessary soil moisture to ensure survival of the seedlings.

5.3 ດິນ

ຄວາມເລິກ ຂອງດິນສະເລ່ຍ:
  • ຕື້ນຫຼາຍ (0-20 ຊັງຕີແມັດ)
  • ຕື້ນ (21-50 ຊຕມ)
  • ເລີກປານກາງ (51-80 ຊຕມ)
  • ເລິກ (81-120 ຊມ)
  • ເລິກຫຼາຍ (> 120 cm)
ເນື້ອດິນ (ໜ້າດິນ):
  • ຫຍາບ / ເບົາ (ດິນຊາຍ)
ເນື້ອດິນ (ເລິກຈາກໜ້າດິນ ລົງໄປຫຼາຍກວ່າ 20 ຊັງຕິແມັດ):
  • ຫຍາບ / ເບົາ (ດິນຊາຍ)
ຊັ້ນອິນຊີວັດຖຸ ເທິງໜ້າດິນ:
  • ຕໍາ່ (<1 %)

5.4 ມີນໍ້າ ແລະ ຄຸນນະພາບ

ລະດັບ ນໍ້າໃຕ້ດິນ:

< 5 ແມັດ

ການມີນໍ້າ ເທິງໜ້າດິນ:

ທຸກຍາກ / ບໍ່ມີ

ຄຸນນະພາບນໍ້າ (ບໍ່ມີການບໍາບັດ):

ບໍ່ມີນໍ້າດື່ມ (ຮຽກຮ້ອງໃຫ້ມີການບຳບັດນ້ຳ)

ມີບັນຫາ ກ່ຽວກັບນໍ້າເຄັມບໍ່?

ແມ່ນ

ລະບຸ ຊະນິດ:

Many bores and wells cannot be used due to Salinity problems. Before planting, it is wise to make sure soil salinity is not problematic in areas identified.

ເກີດມີນໍ້າຖ້ວມ ໃນພື້ນທີ່ບໍ່?

ແມ່ນ

ເປັນປົກກະຕິ:

ຕອນ

ຄວາມຄິດເຫັນ ແລະ ຂໍ້ກໍານົດ ເພີ່ມເຕີມ ກ່ຽວກັບ ຄຸນນະພາບ ແລະ ປະລິມານ ຂອງນ້ຳ:

Water quality and quantity are major issues for the area. There are few if any reliable water sources in the area and most communities depend on wells dug in the river bottoms to supply their water.

5.5 ຊີວະນາໆພັນ

ຄວາມຫຼາກຫຼາຍ ທາງສາຍພັນ:
  • ປານກາງ
ຄວາມຫຼາກຫຼາຍ ທາງດ້ານ ທີ່ຢູ່ອາໃສ ຂອງສິ່ງທີ່ມີຊີວິດ:
  • ຕໍ່າ
ຄວາມຄິດເຫັນ ແລະ ລັກສະນະສະເພາະ ເພີ່ມເຕີມກ່ຽວກັບ ຊີວະນາໆພັນ:

The area is devoid of most wild animals due to the years of war the country experienced during the second half of the 20th century.

5.6 ຄຸນລັກສະນະ ຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ ທີ່ໄດ້ນໍາໃຊ້ເຕັກໂນໂລຢີ

ຢູ່ປະຈຳ ຫຼື ເຄື່ອນຍ້າຍຕະຫຼອດ:
  • ແບບເຄີ່ງຂັງ-ເຄີ່ງປ່ອຍ
ລະບົບ ການຕະຫຼາດ ແລະ ຜົນຜະລິດ:
  • ກຸ້ມຕົນເອງ (ພໍພຽງ)
ລາຍຮັບ ທີ່ບໍ່ໄດ້ມາຈາກ ການຜະລິດ ກະສິກໍາ:
  • 10-50 % ຂອງລາຍຮັບທັງໝົດ
ລະດັບຄວາມຮັ່ງມີ:
  • ທຸກ​ຍາກ​ຫຼາຍ
ບຸກຄົນ ຫຼື ກຸ່ມ:
  • ບຸກຄົນ / ຄົວເຮືອນ
ລະດັບ ການຫັນເປັນກົນຈັກ:
  • ການໃຊ້ແຮງງານຄົນ
ເພດ:
  • ຜູ້ຍິງ
  • ຜູ້ຊາຍ
ອາຍຸ ຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ:
  • ຊາວໜຸ່ມ
  • ໄວ​ກາງ​ຄົນ
ໃຫ້ລະບຸ ຄຸນລັກສະນະ ຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ:

The communities are still traditional though are currently being influenced by the globalisation process.

5.7 ເນື້ອທີ່ສະເລ່ຍຂອງດິນ ທີ່ຜູ້ນຳໃຊ້ທີ່ດິນ ໃຊ້ເຮັດເຕັກໂນໂລຢີ

  • <0.5 ເຮັກຕາ
  • 0.5-1 ເຮັກຕາ
  • 1-2 ເຮັກຕາ
  • 2-5 ເຮັກຕາ
  • 5-15 ເຮັກຕາ
  • 15-50 ເຮັກຕາ
  • 50-100 ເຮັກຕາ
  • 100-500 ເຮັກຕາ
  • 500-1,000 ເຮັກຕາ
  • 1,000-10,000 ເຮັກຕາ
  • > 10,000 ເຮັກຕາ
ຖືໄດ້ວ່າ ເປັນຂະໜາດນ້ອຍ, ກາງ ຫຼື ໃຫຍ່ (ອີງຕາມເງື່ອນໄຂ ສະພາບຄວາມເປັນຈິງ ຂອງທ້ອງຖີ່ນ)? :
  • ຂະໜາດໃຫຍ່
ຄວາມຄິດເຫັນ:

Agricultural plots are considered private and are usually between 1 to 2 hectares, though grazing land, which makes up the majority of the area, is still commonly owned and covers vast areas.

5.8 ເຈົ້າຂອງທີ່ດິນ, ສິດໃຊ້ທີ່ດິນ, ແລະ ສິດທິການນໍາໃຊ້ນໍ້າ

ເຈົ້າຂອງດິນ:
  • ຊຸມຊົນ / ບ້ານ
ສິດທິ ໃນການນໍາໃຊ້ທີ່ດິນ:
  • ເປີດກວ້າງ (ບໍ່ມີການຈັດຕັ້ງ)
ສິດທິ ໃນການນໍາໃຊ້ນໍ້າ:
  • ເປີດກວ້າງ (ບໍ່ມີການຈັດຕັ້ງ)

5.9 ການເຂົ້າເຖິງການບໍລິການ ແລະ ພື້ນຖານໂຄງລ່າງ

ສຸຂະພາບ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ການສຶກສາ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ການຊ່ວຍເຫຼືອ ດ້ານວິຊາການ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ການຈ້າງງານ (ຕົວຢ່າງ, ການເຮັດກິດຈະກໍາອື່ນ ທີ່ບໍ່ແມ່ນ ການຜະລິດກະສິກໍາ):
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ຕະຫຼາດ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ພະລັງງານ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ຖະໜົນຫົນທາງ ແລະ ການຂົນສົ່ງ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ການດື່ມນໍ້າ ແລະ ສຸຂາພິບານ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ
ການ​ບໍ​ລິ​ການ​ ທາງ​ດ້ານ​ການ​ເງິນ:
  • ທຸກຍາກ
  • ປານກາງ
  • ດີ

6. ຜົນກະທົບ ແລະ ລາຍງານສະຫຼຸບ

6.1 ການສະແດງຜົນກະທົບ ພາຍໃນພື້ນທີ່ ທີ່ໄດ້ຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ

ຜົນກະທົບທາງເສດຖະກິດສັງຄົມ

ການຜະລິດ

ການຜະລິດອາຫານສັດ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Low rangeland production

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Slight improvement

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Difficult to measure. Rehabilitation works and the management plans for the rangeland areas have led to some improvement, though the droughts affecting the area during the interventions significantly affected rangeland fodder production.

ຄຸນນະພາບຂອງອາຫານສັດ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

No crop residues or fodder plantings used

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Crop residues and fodder plantings incorporated in cropping areas

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The process allowed Project Technicians to educate communities on the use of crop residues as fodder and the planting of multiuse trees within cropping areas to provide green fodder in the dry season. The reintroduction of drought tolerant, quality indigenous grasses should also lead an increase in fodder production over the coming year.

ຜົນຜະລິດຂອງສັດ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

No planning for dry season grazing, apart from transhumance movements

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Crop residues and other cultivated forages produced for those animals that stay

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The transhumance movements of livestock are still seen as the most adequate solution to changes in natural rangeland production, though most families leave behind some animals with the main family unit. These animals are now receiving the quality feed they need to remain productive and healthy.

ການຈັດການຄຸ້ມຄອງທີ່ດິນ

ອຸປະສັກ
ເຮັດໃຫ້ງ່າຍຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

No management plans in place for commonly managed natural resources

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Participatory land management plans have been negociated and agreed

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Simplified land management plans based on traditional livestock movements and cropping seasons have been negotiated and agreed by local stakeholders and municipal Administrators.

ມີນໍ້າ ແລະ ຄຸນນະພາບ

ນໍ້າດື່ມ ມີຄຸນນະພາບ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Livestock and communities drink from same water

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Separate water drinking points for livestock and community

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Unrestricted access of livestock to community domestic water points led to waterborne diseases and poor water quality. Separating livestock and domestic use has improved community health.

ມີນໍ້າ ໃຫ້ສັດລ້ຽງ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

In addition to restricting livestock access to main water bodies, new drinking troughs have been built with community support.

ຄຸນນະພາບ ຂອງນໍ້າ ສໍາລັບລ້ຽງສັດ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

By separating livestock drinking points and domestic water points, waterborne illnesses have been reduced. In at least one area a water tank and new drinking trough have been built with community support.

ຜົນກະທົບດ້ານວັດທະນາທໍາສັງຄົມ

ຄວາມຮູ້ກ່ຽວກັບ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ / ການເຊື່ອມໂຊມຂອງດິນ

ຫຼຸດຜ່ອນ
ປັບປຸງ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

No education or training on land degradation

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Education and training on land degradation issues and rehabilitation methods

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The majority of communities that have gone through the process now understand how poor land management leads to land degradation and steps they can take to reduce it.

ຜົນກະທົບຕໍ່ລະບົບນິເວດ

ວົງຈອນນໍ້າ / ນໍ້າ

ປະລິມານນໍ້າ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Improved ground cover and the return of riparian vegetation would increase infiltration rates and decrease evapotranspiration rates and restore the micro water cycle. But this is also a long term process.

ຄຸນນະພາບນໍ້າ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Low

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Low in short term, improved in long term

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Revegetation of river plains and river banks should lead to improved water quality though it will be a long term effect if the rehabilitation areas are respected.

ການໄຫຼ ຂອງນໍ້າໜ້າດິນ

ເພີ່ມຂຶ້ນ
ຫຼຸດລົງ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

No method to deal with the high surface runoff rates in the area

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

A method has been devised for reducing surface runoff rates.

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The 'leaky weir' method (Rehabilitation method 3) has shown promise over the duration of the Project and could be applied at other landscape levels to reduce surface runoff.

ດິນ

ການປົກຄຸມຂອງດິນ

ຫຼຸດຜ່ອນ
ປັບປຸງ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The reintroduction of native grasses in the area should lead to improved ground cover, binding the soil and reducing erosion rates.

ການສູນເສຍດິນ

ເພີ່ມຂຶ້ນ
ຫຼຸດລົງ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The reintroduction of native grasses in the area should lead to improved ground cover ratios, binding the soil and reducing erosion rates.

ວົງຈອນ ຂອງສານອາຫານໃນດິນ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Proper livestock management also ensures that manure is properly and evenly distributed in the field.

ຊີວະນານາພັນ: ສັດ, ພືດ

ການປົກຫຸ້ມຂອງພືດ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Reduced number of poor quality grass species

ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ:

Communities capacitated in plant multiplication methods

ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

Apart from the rehabilitation works themselves, the local communities have been capacitated with methods to approach and deal with land degradation.

ມວນຊີວະພາບ / ຢູ່ເທິງຊັ້ນດິນ C

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ

ຄວາມຫຼາກຫຼາຍຂອງພືດ

ຫຼຸດລົງ
ເພີ່ມຂຶ້ນ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The reintroduction of native and leguminous plants has improved plant diversity both within rehabilitation areas and cultivated lands.

ການຫຼຸດຜ່ອນ ຄວາມສ່ຽງ ຈາກໄພພິບັດ ແລະ ອາກາດປ່ຽນແປງ

ຜົນກະທົບ ຂອງໄພແຫ້ງແລ້ງ

ເພີ່ມຂຶ້ນ
ຫຼຸດລົງ

ການປ່ຽນແປງ ອາກາດ ໃນວົງແຄບ

ຮ້າຍແຮງຂຶ້ນ
ປັບປຸງ
ຄວາມຄິດເຫັນ / ລະບຸແຈ້ງ:

The works around the water points over time should lead to increase in vegetative cover, shade, habitat and reduced temperatures.

6.2 ຜົນກະທົບທາງອ້ອມ ຈາກການນໍາໃຊ້ເຕັກໂນໂລຢີ

ການປ້ອງກັນ / ຄວາມອາດສາມາດ ການກັ່ນຕອງ

ຫຼຸດຜ່ອນ
ປັບປຸງ

6.3 ການປ້ອງກັນ ແລະ ຄວາມບອບບາງ ຂອງເຕັກໂນໂລຢິ ໃນການປ່ຽນແປງສະພາບດິນຟ້າອາກາດ ແລະ ກ່ຽວຂ້ອງກັບອາກາດທີ່ມີການປ່ຽນແປງທີ່ຮຸນແຮງ / ໄພພິບັດທາງທໍາມະຊາດ (ຮັບຮູ້ໄດ້ໂດຍຜູ້ນໍາໃຊ້ທີ່ດິນ)

ການປ່ຽນແປງດິນຟ້າອາກາດ ເທື່ອລະກ້າວ

ການປ່ຽນແປງດິນຟ້າອາກາດ ເທື່ອລະກ້າວ
ລະດູການ ເພີ່ມຂື້ນ ຫຼື ຫຼຸດລົງ ການນໍາໃຊ້ ເຕັກໂນໂລຢີ ສາມາດ ຮັບມື ໄດ້ຄືແນວໃດ?
ປະລິມານນໍ້າຝົນປະຈໍາປີ ຫຼຸດລົງ ດີ
ປະລິມານນໍ້າຝົນຕາມລະດູການ ລະດູໃບໄມ້ປົ່ງ ຫຼຸດລົງ ດີ

6.4 ການວິເຄາະຕົ້ນທຶນ ແລະ ຜົນປະໂຫຍດ

ຈະເຮັດປະໂຫຍດເພື່ອປຽບທຽບກັບຄ່າໃຊ້ຈ່າຍກັບສິ່ງກໍ່ສ້າງ (ຈາກທັດສະນະຂອງຜູ້ນຳໃຊ້ທີ່ດິນ) ໄດ້ແນວໃດ?
ຜົນຕອບແທນ ໃນໄລຍະສັ້ນ:

ປານກາງ

ຜົນຕອບແທນ ໃນໄລຍະຍາວ:

ຜົນກະທົບທາງບວກ

ຈະໄດ້ຮັບຜົນປະໂຫຍດເມື່ອປຽບທຽບກັບ / ຄ່າໃຊ້ຈ່າຍໃນການບຳລຸງຮັກສາທີເ່ກີດຂື້ນອິກ (ຈາກທັດສະນະຄະຕິຂອງຜູ້ນຳໃຊ້ທີ່ດິນ) ໄດ້ແນວໃດ?
ຜົນຕອບແທນ ໃນໄລຍະສັ້ນ:

ປານກາງ

ຜົນຕອບແທນ ໃນໄລຍະຍາວ:

ຜົນກະທົບທາງບວກ

6.5 ການປັບຕົວຮັບເອົາເຕັກໂນໂລຢີ

  • ກໍລະນີດຽວ / ການທົດລອງ
ທັງໝົດນັ້ນ ແມ່ນໃຜ ໄດ້ປັບຕົວເຂົ້າ ໃນການນໍາໃຊ້ ເຕັກໂນໂລຢີ, ມີຈັກຄົນ ທີ່ສາມາດເຮັດເອງໄດ້, ຕົວຢ່າງ, ປາດສະຈາກ ການຊ່ວຍເຫຼືອ ທາງດ້ານອຸປະກອນ / ການຈ່າຍເປັນເງິນ?
  • 0-10%

6.6 ການປັບຕົວ

ໄດ້ມີການດັດປັບ ເຕັກໂນໂລຢີ ເພື່ອໃຫ້ແທດເໝາະກັບເງື່ອນໄຂ ການປ່ຽນແປງບໍ?

ບໍ່ແມ່ນ

6.7 ຈຸດແຂງ / ຂໍ້ດີ / ໂອກາດ ໃນການນໍາໃຊ້ ເຕັກໂນໂລຢີ

ຈຸດແຂງ / ຂໍ້ດີ / ໂອກາດໃນການນໍາໃຊ້ທີ່ດິນ
Communities learn about plants' role in the wider ecosystem, how to select and multiply key fruit, fodder or timber species and should see an increase in their horticultural and livestock production, leading to improved nutrition or income.
Done properly, it can be a cost-effective and reliable way to produce the plants needed within family units.
ຈຸດແຂງ / ຈຸດດີ / ໂອກາດ ຈາກທັດສະນະຂອງຜູ້ປ້ອນຂໍ້ມູນ ຫຼື ບຸກຄົນສຳຄັນ
When the plants are produced in collaboration with the local pastoral communities, the benefits are wide ranging, promoting everything from environmental awareness to technical and practical knowledge.
It remains a cost-effective way of improving key productive species and increasing community resilience.
Increasing biomass and introducing better management cycles contribute to reducing land degradation and improve nutrient and energy cycling.

6.8 ຈຸດອ່ອນ / ຂໍ້ເສຍ / ຄວາມສ່ຽງ ໃນການນໍາໃຊ້ ເຕັກໂນໂລຢີ ແລະ ວິທີການແກ້ໄຂບັນຫາ

ຈຸດອ່ອນ / ຂໍ້ເສຍ / ຄວາມສ່ຽງໃນມຸມມອງຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ ມີວິທີການແກ້ໄຂຄືແນວໃດ?
Can require stable supply of water, and labour costs can increase if water sources are not easily accessible. Locate nurseries near reliable and accessible water sources.
Can require permanent residence, so as to be able to care for plants until they are developed and placed in the ground at the proper date in the calendar (before or during rainy season). Not easy in nomadic cultures.
Early attempts often fail to produce lasting results. Concentrate early efforts on small experimental plots so as to fine-tune planting methods and timing.
ຈຸດອ່ອນ/ຂໍ້ບົກຜ່ອງ/ຄວາມສ່ຽງ ຈາກທັດສະນະຂອງຜູ້ປ້ອນຂໍ້ມູນ ຫຼື ບຸກຄົນສຳຄັນ ມີວິທີການແກ້ໄຂຄືແນວໃດ?
The technology is usually not suitable for large areas of land (>1,000 hectares). Compliment any rehabilitation efforts with improved management plans which are developed with stakeholder input and approval.
Plant losses are typically high, especially if rains fail to arrive, or if the year is abnormally dry. Watch weather forecast to try and focus planting campaigns on those days with a high probability of rain.
Local species are often not valued by local officials and technicians, leading to a predominance of exotic species in rehabilitation works. Undertake awareness and training sessions which highlight the value and uses of native species with local land users and administrative officials.

7. ເອກະສານອ້າງອີງ ແລະ ການເຊື່ອມຕໍ່

7.1 ວິທີການ / ແຫຼ່ງຂໍ້ມູນ

  • ການໄປຢ້ຽມຢາມພາກສະໜາມ, ການສໍາຫຼວດພາກສະໜາມ

The Project has a number of activities in the communities where the technology was used so there were numerous visits and interviews.

  • ການສໍາພາດ ຜູ້ນໍາໃຊ້ທີ່ດິນ

Various information and survey methods were used throughout the RETESA Project, providing a solid basis from which to involve landusers and SLM specialists in decisionmaking processes.

  • ສໍາພາດ ຊ່ຽວຊານ ການຄຸ້ມຄອງ ດິນແບບຍືນຍົງ

3 SLM specialists.

ເມື່ອໃດທີ່ໄດ້ສັງລວມຂໍ້ມູນ (ຢູ່ພາກສະໜາມ)?

15/05/2017

7.3 Links to relevant online information

ຫົວຂໍ້ / ພັນລະນາ:

FAO in Action: Using indigenous knowledge to reverse land degradation in Angola.

URL:

http://www.fao.org/in-action/using-indigenous-knowledge-to-reverse-land-degradation-in-angola/en/

ຂໍ້ມູນການເຊື່ອມຕໍ່ ແລະ ເນື້ອໃນ

ຂະຫຍາຍທັງໝົດ ຍຸບທັງໝົດ

ເນື້ອໃນ