1.2 ລາຍລະອຽດ ການຕິດຕໍ່ ຂອງບຸກຄົນທີ່ຊັບພະຍາກອນ ແລະ ສະຖາບັນ ການມີສ່ວນຮ່ວມ ໃນການປະເມີນຜົນ ແລະ ເອກະສານ ຂອງວິທີທາງ

ຊື່ຂອງໂຄງການ ທີ່ອໍານວຍຄວາມສະດວກ ໃນການສ້າງເອກກະສານ ຫຼື ປະເມີນດ້ານແນວທາງ (ຖ້າກ່ຽວຂ້ອງ)

Strengthening of Livelihoods through Climate Change Adaptation in Kyrgyzstan and Tajikistan

ຊື່ຂອງ ສະຖາບັນການຈັດຕັ້ງ ທີ່ອໍານວຍຄວາມສະດວກ ໃນການສ້າງເອກກະສານ ຫຼື ປະເມີນແນວທາງ (ຖ້າກ່ຽວຂ້ອງ)

GIZ Tajikistan (GIZ Tajikistan) - ຕາຈິກິສະຕານ

1.3 ເງື່ອນໄຂ ຂອງການນໍາໃຊ້ເອກກະສານຂໍ້ມູນ ຂອງ WOCAT

ຜູ້ສັງລວມ ແລະ ບັນດາຜູ້ຕອບແບບສອບຖາມ ຍອມຮັບໃນເງື່ອນໄຂ ການນໍາໃຊ້ຂໍ້ມູນເອກະສານ ທີ່ສ້າງຂື້ນ ໂດຍຜ່ານ ອົງການ WOCAT:

ແມ່ນ

1.4 ເອກະສານອ້າງອີງ (ຫຼາຍ) ກັບແບບສອບຖາມ (ຫຼາຍ) ເຕັກໂນໂລຢີ ຂອງດ້ານການຄຸ້ມຄອງ ດິນແບບຍືນຍົງ

2.1 ການອະທິບາຍ ໂດຍຫຍໍ້ ຂອງວິທີທາງ

A site affected by a debris flow was rehabilitated by joint communal work and integrated preventive measures addressing the upper catchment as well as the valley and the debris conus were implemented in collaboration of community, individual farmers, Committee of Emergency Situations and forestry enterprise.

2.2 ການອະທິບາຍ ລາຍລະອຽດ ຂອງວິທີທາງ

ການອະທິບາຍ ລາຍລະອຽດ ຂອງວິທີທາງ:

Local people in many parts of Tajikistan, among these the project region at the northern main slope of the Turkestan range, report about formerly unknown flashfloods and debris flows, even in areas where such events are not remembered. Also relief, soil and vegetation often confirm that such sites for long times had not been transformed by these forces. The occurrence of flashfloods and debris flows in formerly not affected areas, unusual seasons or an increase in frequency and destructiveness of such events can be attributed to land degradation in upper catchment areas in combination with climate change impact.

The degradation of the vegetation in upper catchments has contributed to reduced infiltration of water and high and fast surface runoff. Important elements of this degradation are overgrazing and deforestation. Overgrazing and out of season grazing cause the reduction of the protective plant cover and the multiple trails of livestock with compressed soil reduce infiltration and increase the surface runoff. Deforestation is typically related to intensive livestock grazing, in particular by goats, as intensive browsing prevents the regeneration of shrub and tree vegetation. In upper catchments affected by these processes during heavy rainfall and snow melt large amounts of water concentrate in small valleys and take with them large amounts of soil and gravel. The deforestation in valleys contributes to the intensity of such flashfloods and debris flows.

The frequency and intensity of these events is increasingly exacerbated by the impact of climate change. The already visible trends and predictions show higher levels of aridity, higher temperatures during the vegetation season, reduced overall precipitation in catchment areas – all affecting the retention potential of upper catchment areas – and more irregular rainfall patterns, reduced snow packs and accelerated snow melt as well as the loss of glaciers as buffers of water flow. These factors all contribute to a higher frequency and intensity of flashflood and debris flows and their occurrence in previously not or less affected areas.

Near the village Shamoli in Shakhriston district, as in many other locations, such a debris flow made a road impassable and has destroyed pasture lands and five hectares of arable lands belonging to several farmers with another 10 ha being at risk in case such events occur again. Local people assisted by the Committee of Emergency Situations opened and cleaned the road. The developed in collaboration with experts an integrated approach for rehabilitating the affected lands and reducing the disaster risk. The approach included the following elements:
•Blocking of gullies with planting of willows for reducing sediment load in case of future flashfloods;
•Agreement with the forestry enterprise about general regulation of grazing and tree planting (specifics to be decided by the forestry enterprise);
•Joint communal work (hashar) for cleaning affected arable lands from debris;
•Fencing of 4 ha lands in the valley leased by one farmer from the forestry enterprise for rehabilitation of protective vegetation and sustainable land use (orchard and hay making);
•Construction of reservoir for water collection from spring and use for drip irrigation of trees planted at the debris conus in the opening of the valley.

The approach brought together the Committee of Emergency Situations, the administrative communities, affected local people and the forestry enterprise. Assisted by experts provided by the project, the situation was jointly analyzed; risks identified and the integrated intervention planned. The project assisted with technical planning, construction supervision, purchase and transportation of construction materials. The community contributed about 30% of the overall costs, mainly in form of voluntary communal work, the so called hashar. One farmer leased the most critical area at the opening of the valley and took the responsibility for the maintenance of the area in exchange for the opportunity to use hay and fruits from the planted trees.

The approach is generally replicable. But in most such sites the upper catchment areas belong to different communities, often to different districts and substantial parts are located in neighboring Kyrgyzstan. Therefore addressing the degradation of these areas and a reduction of disaster risk through integrated watershed management in the entire catchments will require more collaboration across administrative boundaries and even national borders.

2.3 ຮູບພາບຂອງແນວທາງ

2.5 ປະເທດ / ເຂດ / ສະຖານທີ່ບ່ອນທີ່ແນວທາງໄດ້ຖືກນໍາໃຊ້

2.6 ວັນທີເລີ່ມຕົ້ນ ແລະ ສິ້ນສຸດ ການຈັດຕັ້ງປະຕີບັດ ວິທີທາງ

2.7 ປະເພດຂອງແນວທາງ

• ພາຍໃຕ້ໂຄງການ / ແຜນງານ

2.8 ເປົ້າໝາຍ / ຈຸດປະສົງຫຼັກ ຂອງການຈັດຕັ້ງປະຕິບັດ ວິທີທາງ

Rehabilitation of land affected by debris flow and reduction of risk of future events.

2.9 ເງື່ອນໄຂອໍານວຍ ຫຼື ຂັດຂວາງການປະຕິບັດຂອງເຕັກໂນໂລຢີ / ເຕັກໂນໂລຢີການນໍາໃຊ້ຕາມແນວທາງ

3.1 ຜູ້ມີສ່ວນຮ່ວມ ໃນວິທີທາງ ແລະ ພາລະບົດບາດ ຂອງເຂົາເຈົ້າ

3.2 ການມີສ່ວນຮ່ວມຂອງຜູ້ນໍາໃຊ້ທີ່ດິນໃນທ້ອງຖິ່ນ / ຊຸມຊົນທ້ອງຖິ່ນໃນໄລຍະທີ່ແຕກຕ່າງກັນຂອງແນວທາງ

	ການລວບລວມ ເອົາຜູ້ນໍາໃຊ້ດິນ ໃນທ້ອງຖິ່ນ / ຊຸມຊົນທ້ອງຖິ່ນ	ໃຫ້ລະບຸ ຜູ້ໃດທີ່ມີສ່ວນຮ່ວມ ໃນແຕ່ລະກິດຈະກໍາ?
ການເລີ່ມຕົ້ນ / ແຮງຈູງໃຈ	ການຮ່ວມມື	Local community members, asking community leadership and GIZ staff for assistance to address impact of debris flow
ການວາງແຜນ	ການຮ່ວມມື	Involvement of community members in planning
ການປະຕິບັດ		Local community members carrying out works through traditional voluntary community work ("hashar").
ຕິດຕາມກວດກາ / ການປະເມີນຜົນ		Local farmer maintaining the planted area controls condition of irrigation system and trees.
maintenance		Local farmer maintaining the planted area.

3.4 ການຕັດສິນໃຈກ່ຽວກັບການຄັດເລືອກເຕັກໂນໂລຢີຂອງການຄຸ້ມຄອງທີ່ດິນແບບຍືນຍົງ / ເຕັກໂນໂລຢີ

ລະບຸ ຄົນທີ່ຕັດສິນໃຈ ກ່ຽວກັບການຄັດເລືອກຂອງ ເຕັກໂນໂລຢີ / ເຕັກໂນໂລຢີ ຈະໄດ້ຮັບການປະຕິບັດ:

• ພາກສ່ວນກ່ຽວຂ້ອງທັງໝົດ, ເປັນສ່ວນໜຶ່ງ ຂອງວິທີທາງແບບມີສ່ວນຮ່ວມ

Specify on what basis decisions were made:

• ປະເມີນເອກກະສານ ຄວາມຮູ້ກ່ຽວກັບ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ (ຫຼັກຖານທີ່ຊ່ວຍໃນການຕັດສິນໃຈ)
• ປະສົບການສ່ວນບຸກຄົນ ແລະ ຄວາມຄິດເຫັນ (ທີ່ບໍ່ເປັນເອກກະສານ)

4.1 ການສ້າງຄວາມສາມາດ / ການຝຶກອົບຮົມ

ຜູ້ນໍາໃຊ້ທີ່ດິນ ຫຼື ພາກສ່ວນກ່ຽວຂ້ອງອື່ນໆ ໄດ້ຮັບການຝຶກອົບຮົມບໍ່?

ບໍ່ແມ່ນ

4.2 ການບໍລິການໃຫ້ຄໍາປຶກສາ

ເຮັດຜູ້ໃຊ້ທີ່ດິນມີການເຂົ້າເຖິງການບໍລິການໃຫ້ຄໍາປຶກສາ?

ແມ່ນ

ອະທິບາຍ / ຄວາມຄິດເຫັນ:

Not of specific relevance for this approach.

4.3 ສະຖາບັນການສ້າງຄວາມເຂັ້ມແຂງ (ການພັດທະນາອົງການຈັດຕັ້ງ)

ສະຖາບັນ ໄດ້ຮັບການສ້າງຕັ້ງຂື້ນ ຫຼື ໄດ້ຮັບການສ້າງຄວາມເຂັ້ມແຂງ ໂດຍການຈັດຕັ້ງປະຕິບັດ ວິທີທາງບໍ່?

• ມີ, ໜ້ອຍໜຶ່ງ

ລະບຸ ທາງສະຖາບັນ ໄດ້ສ້າງຄວາມເຂັ້ມແຂງ ໃນລະດັບໃດ (ຫຼາຍ):

• ທ້ອງຖິ່ນ

ອະທິບາຍ ສະຖາບັນການຈັດຕັ້ງ, ພາລະບົດບາດ ແລະ ໜ້າທີ່ຮັບຜິດຊອບ, ສະມາຊິກ ແລະ ອື່ນໆ.

Existing community institutions have been strengthened through joint successful implementation of the works and the need for further collaboration.

ລະບຸ ປະເພດ ຂອງສະໜັບສະໜູນ:

• ທາງດ້ານການເງິນ
• ການສ້າງຄວາມອາດສາມາດ / ການຝຶກອົບຮົມ
• ອຸປະກອນ

ໃຫ້ລາຍລະອຽດເພີ່ມເຕີມ:

Fencing, materials of irrigation system, technical advice.

4.4 ຕິດຕາມກວດກາ ແລະ ປະເມີນຜົນ

ການຈັດຕັ້ງປະຕິບັດ ວິທີທາງ ໄດ້ມີການປະເມີນຜົນ ແລະ ຕິດຕາມບໍ?

ແມ່ນ

ຖ້າແມ່ນ, ເອກກະສານສະບັບນີ້ ແມ່ນໄດ້ນໍາໃຊ້ເຂົ້າໃນການຕິດຕາມ ແລະ ປະເມີນຜົນບໍ່?

ບໍ່ແມ່ນ

4.5 ການຄົ້ນຄວ້າ

ນີ້້ແມ່ນສ່ວນໜຶ່ງ ການຄົ້ນຄວ້າ ຂອງວິທີທາງບໍ່?

ບໍ່ແມ່ນ

5.1 ງົບປະມານປະຈໍາປີ ສໍາລັບວິທີທາງ ຂອງການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ

ຖ້າຫາກບໍ່ຮູ້ຈັດງົບປະມານທີ່ແນ່ນອນ ແມ່ນໃຫ້ປະມານເອົາ:

• 2,000-10,000

ຄໍາເຫັນ (ຕົວຢ່າງ: ແຫຼ່ງຂໍ້ມູນຫຼັກ ຂອງການສະໜອງທຶນ / ຜູ້ໃຫ້ທຶນທີ່ສໍາຄັນ):

Government of Germany, implemented via Deutsche Gesellschaft für Internationale Zusammenarbeit (GIZ). The approach has been implemented in the frame of a much larger program and the specific budget for the SLM component of the Approach cannot be determined.

5.2 ການສະໜັບສະໜູນ ທາງດ້ານການເງິນ / ອຸປະກອນ ສະໜອງໃຫ້ແກ່ຜູ້ນໍາທີ່ດິນ

ຜູ້ນໍາໃຊ້ດິນ ໄດ້ຮັບການສະໜັບສະໜູນ ທາງດ້ານ ການເງິນ / ອຸປະກອນ ໃນການຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີບໍ?

ແມ່ນ

ຖ້າແມ່ນ, ໃຫ້ລະບຸປະເພດ (ຫຼາຍ) ຂອງການສະໜັບສະໜູນ, ເງື່ອນໄຂ ແລະ ຜູູ້ສະໜອງ (ຫຼາຍ):

Technical planning and supervision, procurement of materials and transportation funded by GIZ.

5.3 ເງິນສົມທົບສໍາລັບການນໍາໃຊ້ສະເພາະປັດໃຈຂາເຂົ້າໃນການຜະລີດກະສິກໍາ (ລວມທັງແຮງງານ)

• ບໍ່ມີ

ຖ້າແຮງງານ ຂອງຜູ້ນໍາໃຊ້ດິນ ໄດ້ຮັບການສະໜັບສະໜູນ ປັດໃຈຂາເຂົ້າ, ແມ່ນບໍ່:

• ການອາສາ

5.4 ສິນເຊື່ອ

ໄດ້ປ່ອຍສິນເຊື່ອ ສະໜອງໃຫ້ພາຍໃຕ້ ວິທີການສໍາລັບກິດຈະກໍາ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນນຍົງບໍ່?

ບໍ່ແມ່ນ

5.5 ສິ່ງຈູງໃຈ ຫຼື ເຄື່ອງມືອື່ນໆ

ການສົ່ງເສີມ ຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ ໃນການຄຸ້ມຄອງ ດິນແບບຍືນຍົງ ໄດ້ສະໜອງສິ່ງກະຕຸກຊຸກຍູ້ບໍ່?

ແມ່ນ

ຖ້າແມ່ນ, ໃຫ້ລະບຸ:

The farmer managing the site in the valley, where trees have been planted, can use the fruits and the hay produced from the site. This is the key incentive for him to carry out all maintenance.

6.1 ຜົນກະທົບຂອງແນວທາງ

6.2 ແຮງຈູງໃຈຫຼັກຂອງຜູ້ນໍາໃຊ້ທີ່ດິນໃນການປະຕິບັດການຄຸ້ມຄອງທີ່ດິນແບບຍືນຍົງ

6.3 ຄວາມຍືນຍົງຂອງກິດຈະກໍາວິທີທາງ

ຜູ້ນໍາໃຊ້ ທີ່ດິນ ສາມາດສືບຕໍ່ ການຈັດຕັ້ງປະຕິບັດ ຜ່ານວິທີທາງໄດ້ບໍ່ (ໂດຍປາດສະຈາກ ການຊ່ວຍເຫຼືອ ຈາກພາກສ່ວນພາຍນອກ)?

• ແມ່ນ

6.4 ຈຸດແຂງ / ຂໍ້ດີ ຂອງວິທີທາງ

ຈຸດແຂງ / ຂໍ້ດີ / ໂອກາດໃນການນໍາໃຊ້ທີ່ດິນ
Rehabilitated lands and reduced risk.
Use of products from critical site, which was planted with fruit trees.

ຈຸດແຂງ / ຈຸດດີ / ໂອກາດ ຈາກທັດສະນະຂອງຜູ້ປ້ອນຂໍ້ມູນ ຫຼື ບຸກຄົນສຳຄັນ
Same as land users' view.
Mobilization of collaboration and joint communal work.

6.5 ຈຸດອ່ອນ / ຂໍ້ເສຍຂອງແນວທາງ ແລະ ວິທີການແກ້ໄຂໃຫ້ເຂົາເຈົ້າ

ຈຸດອ່ອນ / ຂໍ້ເສຍ / ຄວາມສ່ຽງໃນມູມມອງຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ	ມີວິທີການແກ້ໄຂຄືແນວໃດ?
High costs of fencing	External funding.
High costs of irrigation system	External funding.

ຈຸດອ່ອນ ຫຼື ຂໍ້ເສຍ ຫຼື ຄວາມສ່ຽງ ໃນມຸມມອງຂອງ ຜູ້ສັງລວມຂໍ້ມູນ ຫຼື ບັນດາຜູ້ຕອບແບບສອບຖາມ	ມີວິທີການແກ້ໄຂຄືແນວໃດ?
High costs of fencing	External funding; Cheaper temporary electric fencing; Approaches without fencing, based on agreement in the community to prevent livestock damage through herding.
High costs of irrigation system	External funding; Planting of drought resistant trees.

7.1 ວິທີການ / ແຫຼ່ງຂໍ້ມູນ