1.2 ຂໍ້ມູນ ການຕິດຕໍ່ພົວພັນ ຂອງບຸກຄົນທີ່ສໍາຄັນ ແລະ ສະຖາບັນ ທີ່ມີສ່ວນຮ່ວມ ໃນການປະເມີນເອກກະສານ ເຕັກໂນໂລຢີ

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

ເມື່ອໃດທີ່ໄດ້ສັງລວມຂໍ້ມູນ (ຢູ່ພາກສະໜາມ)?

26/01/2018

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

2.1 ຄໍາອະທິບາຍສັ້ນຂອງ ເຕັກໂນໂລຢີ

ການກຳໜົດຄວາມໝາຍ ຂອງເຕັກໂນໂລຢີ:

This 'Rangeland Restoration' technology is part of a 'Holistic Rangeland Management' approach. It involves clearing of invasive vegetation (predominantly Acacia reficiens) and reseeding with grass (Cenchrus ciliaris) and allowing resting and reduced grazing pressure to rehabilitate degraded communal grazing land.

2.2 ການອະທິບາຍ ລາຍລະອຽດ ຂອງເຕັກໂນໂລຢີ

ການພັນລະນາ:

The 'Rangeland Restoration' technology is applied in degraded sites within the 3,100 Ha 'core conservation area' (an central area with minimised grazing pressure designated for tourism) and 'buffer zone' (an area surrounding the 'core conservation area' with reduced grazing pressure) of the Kalama Community Wildlife Conservancy (total area: 9,500 Ha).

The main characteristics are clearing of invasive woody vegetation (predominantly Acacia reficiens) and reseeding with grass (Cenchrus ciliaris). Acacia reficiens (commonly known as red-bark acacia, red thorn or false umbrella tree or thorn) is a native tree or shrub but is considered an invasive species as it can encroach degraded areas with bare and disturbed soil. It is very opportunistic and hardy and can subsequently take over large areas of native vegetation. The invasion can reach a closed or nearly closed canopy with A. reficiens thickets, which are hindering animals to enter and access fodder thus making the area inaccessible for grazing and browsing. Additionally it can be observed that the soil underneath the canopy remains bare and the grass growth seems to be suppressed. As a result the top soil is compacted or forms crusts, which hinder infiltration. During the erratic but heavy rains most of the water flows away as runoff (research in close by areas show that runoff is between 60-80 % of the rainfall) and increases soil erosion and further degradation of the land despite a rather good tree cover. Rangeland grass and fodder productivity in these areas are reduced to a fraction of their potential.
The main activity is the cutting of the trees and shrubs at a height of ~1 m. The main trunks and branches can be used for fencing, temporary house constructions, firewood and charcoal. Most of the cut trees and the remaining branches are used to spread on the bare land where the trees and shrubs are cut. Underneath this dead material the bare soil receives some cover, which creates favorable conditions and microclimate for termites and other fauna in the soil to brake the hard top soil and crust and enable infiltration of the water during the next rains. This allows regrowth of grasses, particularly in the areas protected by the branches. In the following seasons the spread of the grasses can increase also the the area not protected by the branches. Additionally, seeding with Cenchrus ciliaris (buffel-grass or African foxtail grass), a grass species which is native to most of Africa, enhances the growth of a highly valuable fodder grass. Seeds are hand-broadcasted in the treated areas and germinate during the next rainy season. The first greening is visible in the places where the branches and the wood pieces cover the soil. From there the local annual and perennial grasses start colonising and expanding in the following seasons until, ideally, the whole area that has been bare is covered by valuable perennial grasses. Parallel to the cutting and reseeding is reduced grazing pressure and a resting period over at least one dry season, which is facilitated by the fact that treated areas are situated in the core conservation area or in the buffer zone. This involves the cooperation of the members of Kalama Conservancy, who agree to restrict grazing in the buffer zone and more so in the core conservation area. The exact duration that grazing is allowed in each of these two areas varies year to year depending on drought severity and forage availability. Whereas the grazing pressure by livestock can be regulated, there remains uncontrolled grazing by wildlife. The major herbivores are zebra, elephants and a number of different gazelle and antelope species the grazing pressure by wildlife varies but can be substantial at certain times.

Rehabilitating degraded grazing land is the primary purpose of the technology. Other benefits of the technology include: 1) augmented forage availability for the community; 2) increased livestock production; 3) reduced soil erosion and flooding. Land users enjoy these benefits but would like larger areas to be similarly restored. However, the limiting factor is the funding required to pay for labour, which is the major input required for the clearing and reseeding activities. Establishing a market for removing the main stems and producing and selling charcoal is still an opportunity to further explore immediate benefits and cash income in order to pay for the investment into the clearing.

2.3 ຮູບພາບຂອງເຕັກໂນໂລຢີ

2.5 ປະເທດ / ເຂດ / ສະຖານທີ່ບ່ອນທີ່ ເຕັກໂນໂລຢີ ໄດ້ຮັບການນໍາໃຊ້ ແລະ ທີ່ຖືກປົກຄຸມດ້ວຍການປະເມີນຜົນ

2.6 ວັນທີໃນການຈັດຕັ້ງປະຕິບັດ

ໃຫ້ລະບຸປີ ໃນການຈັດຕັ້ງປະຕິບັດ:

2006

ຖ້າຫາກວ່າ ບໍ່ຮູ້ຈັກ ປີທີ່ຊັດເຈນ ແມ່ນໃຫ້ປະມານ ວັນທີເອົາ:

• 10-50 ປີ ຜ່ານມາ

2.7 ການນໍາສະເໜີ ເຕັກໂນໂລຢີ

ໃຫ້ລະບຸ ເຕັກໂນໂລຢີ ໄດ້ຖືກຈັດຕັ້ງປະຕິບັດຄືແນວໃດ?

• ໂດຍຜ່ານໂຄງການ / ການຊ່ວຍເຫຼືອຈາກພາຍນອກ

ຄວາມຄິດເຫັນ (ປະເພດ ໂຄງການ ແລະ ອື່ນໆ):

Acacia reficiens was already selectively cleared traditionally when constructing livestock corrals ('bomas'), but the introduction of more extensive clearing and grass-reseeding to rehabilitate specific areas was facilitated by Northern Rangeland Trust and Grevy's Zebra Trust.

3.1 ຈຸດປະສົງຫຼັກ (ຫຼາຍ) ຂອງເຕັກໂນໂລຢີ

• ຫຼຸດຜ່ອນ, ປ້ອງກັນ, ຟື້ນຟູ ການເຊື່ອມໂຊມຂອງດິນ
• ການອະນຸລັກ ລະບົບນິເວດ
• ປົກປັກຮັກສາ / ການປັບປຸງຊີວະນາໆພັນ

3.2 ປະເພດການນໍາໃຊ້ທີ່ດິນ ໃນປະຈຸບັນ() ທີ່ເຕັກໂນໂລຢີ ໄດ້ຖືກນໍາໃຊ້

3.3 ຂໍ້ມູນເພີ່ມເຕີມກ່ຽວກັບການນໍາໃຊ້ທີ່ດິນ

ການສະໜອງນໍ້າ ໃນພື້ນທີ່ ທີ່ໄດ້ນໍາໃຊ້ ເຕັກໂນໂລຢີ:

• ນໍ້າຝົນ

ຈໍານວນ ລະດູການ ປູກໃນປີໜຶ່ງ:

• 2

ລະບຸ ຊະນິດ:

Rainiy seasons from April to June and from October to December but with high variability in time and amount

ຄວາມໜາແໜ້ນ ຂອງສັດລ້ຽງ (ຖ້າຫາກວ່າກ່ຽວຂ້ອງ):

likely continuously growing till technology was introduced

3.4 ການນໍາໃຊ້ເຕັກໂນໂລຢີ ທີ່ຢູ່ໃນກຸ່ມການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ

• ການຄຸ້ມຄອງສັດລ້ຽງ ແລະ ທົ່ງຫຍ້າລ້ຽງສັດ
• ການປັບປຸງດິນ / ພືດຄຸມດິນ
• ການປັບປຸງແນວພັນພືດ / ແນວພັນສັດ

3.5 ການຂະຫຍາຍເຕັກໂນໂລຢີ

ໃຫ້ລະບຸ ການແຜ່ຂະຫຍາຍ ເຕັກໂນໂລຢີ:

• ນໍາໃຊ້ໃນຈຸດສະເພາະ / ແນໃສ່ນໍາໃຊ້ໃນພື້ນທີ່ຂະໜາດນ້ອຍ

3.6 ມາດຕະການ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ ປະກອບດ້ວຍ ເຕັກໂນໂລຢີ

3.7 ປະເພດດິນເຊື່ອມໂຊມ ຫຼັກທີ່ໄດ້ນໍາໃຊ້ ເຕັກໂນໂລຢີ

3.8 ການປ້ອງກັນ, ການຫຼຸດຜ່ອນ, ຫຼືການຟື້ນຟູຂອງການເຊື່ອມໂຊມຂອງດິນ

ໃຫ້ລະບຸ ເປົ້າໝາຍ ເຕັກໂນໂລຢີ ທີ່ພົວພັນ ກັບຄວາມເຊື່ອມໂຊມຂອງດິນ:

• ຫຼຸດຜ່ອນການເຊື່ອມໂຊມຂອງດິນ
• ການຟື້ນຟູ / ຟື້ນຟູດິນທີ່ຊຸດໂຊມ

4.1 ເຕັກນິກ ໃນການແຕ້ມແຜນວາດ ເຕັກໂນໂລຢີ

4.2 ການແຕ້ມແຜນວາດອະທິບາຍເຕັກນິກ

A total of 279 hectares were treated with this rangeland restoration technology (clearing invasive Acacia reficiens and reseeding with Cenchrus ciliaris). Treated areas were relatively flat (slope < 5%). A. reficiens were cut ~1 m above the ground and well before the onset of the rains to discourage regeneration. C. ciliaris seeds were hand-broadcast at a rate of ~45 kg/Ha.
Holding membership of multiple community conservancies facilitates the movement between wet season and dry season grazing areas. For example, many of the local communities move their livestock to Losesia, in Sera Conservancy, for dry season grazing. These porous boundaries relieve pressure from Kalama Conservancy during some parts of the year, potentially facilitating recovery of treated areas, but also allows neighbouring communities to access treated areas rendering their grazing management challenging.

4.3 ຂໍ້ມູນທົ່ວໄປກ່ຽວກັບການຄິດໄລ່ປັດໃຈຂາເຂົ້າໃນການຜະລິດ ແລະ ມູນຄ່າອື່ນໆ

ລະບຸ ວິທີການ ຄຳໃຊ້ຈ່າຍ ແລະ ປັດໄຈນໍາເຂົ້າ ທີ່ໄດ້ຄິດໄລ່:

• ຕໍ່ພື້ນທີ່ ທີ່ໄດ້ຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ

ສະກຸນເງິນອື່ນໆ / ປະເທດອື່ນໆ (ລະບຸ):

Kenya Shillings

ລະບຸ ອັດຕາແລກປ່ຽນ ຈາກໂດລາ ເປັນເງິນຕາທ້ອງຖີ່ນ (ຖ້າກ່ຽວຂ້ອງ): 1 ໂດລາ =:

101.0

4.4 ການສ້າງຕັ້ງກິດຈະກໍາ

	ກິດຈະກໍາ	ປະເພດ ມາດຕະການ	ໄລຍະເວລາ
1.	Clearing Acacia reficiens (cutting and spreading)	ການບໍາລຸງລ້ຽງ	During dry season, well before the onset of rains to prevent Acacia reficiens regrowth from stump.
2.	Reseeding with Cenchrus ciliaris grass seed	ການບໍາລຸງລ້ຽງ	Prior to the onset of rainy season to maximise germination and establishment of Cenhrus ciliaris..

4.5 ຕົ້ນທຶນ ແລະ ປັດໄຈຂາເຂົ້າທີ່ຈໍາເປັນໃນຈັດຕັ້ງປະຕິບັດ

	ລະບຸ ປັດໃຈ ນໍາເຂົ້າ ໃນການຜະລີດ	ຫົວໜ່ວຍ	ປະລິມານ	ຕົ້ນທຶນ ຕໍ່ຫົວໜ່ວຍ	ຕົ້ນທຶນທັງໝົດ ຂອງປັດໃຈຂາເຂົ້າ ໃນການຜະລິດ	% ຂອງຕົ້ນທຶນທັງໝົດ ທີ່ຜູ້ນໍາໃຊ້ທີ່ດິນ ໃຊ້ຈ່າຍເອງ
ແຮງງານ	Clearing Acacia reficiens	person-days	1200.0	450.0	540000.0
ແຮງງານ	Hand-broadcasting Cenchrus ciliaris seeds	person-days	1200.0	450.0	540000.0
ອຸປະກອນ	Machettes	units	40.0	500.0	20000.0
ວັດສະດຸໃນການປູກ	Cenchrus ciliaris seeds	kg	2520.0	50.0	126000.0
ອື່ນໆ	Transport of workers to and from site	litre	600.0	100.0	60000.0
ຕົ້ນທຶນທັງໝົດ ໃນການຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ					1286000.0

ຖ້າຫາກຜູ້ນຳໃຊ້ທີ່ດິນ ນຳໃຊ້ມູນຄ່າຕ່ຳກວ່າ 100% ໃຫ້ລະບຸ ແມ່ນໃຜເປັນຜູ້ຊ່ວຍ ໃນລາຍຈ່າຍທີ່ເຫຼືອ:

Funding raised by Northern Rangelands Trust and Grezy's Zebra Trust (including USAID and FAO funding).

ຄວາມຄິດເຫັນ:

These are the costs associated a 55 Ha treated area. Six sites of a similar size were treated with similar budgets totalling 279 Ha.

4.6 ບໍາລຸງຮັກສາ / ແຜນຈັດຕັ້ງປະຕິບັດ ກິດຈະກໍາ

ຄວາມຄິດເຫັນ:

No maintenance activities.

4.7 ຄ່າໃຊ້ຈ່າຍ ແລະ ປັດໄຈນໍາເຂົ້າທີ່ຈໍາເປັນສໍາລັບການບໍາລຸງຮັກສາກິດຈະກໍາ / ແຜນປະຕິບັດ (ຕໍ່ປີ)

ຄວາມຄິດເຫັນ:

No maintenance costs.

4.8 ປັດໄຈ ທີ່ສໍາຄັນ ທີ່ສົ່ງຜົນກະທົບ ຕໍ່ຄ່າໃຊ້ຈ່າຍ

ໃຫ້ອະທິບາຍ ປັດໃຈ ທີ່ສົ່ງຜົນກະທົບ ຕໍ່ຕົ້ນທຶນ ໃນການຈັດຕັ້ງປະຕິບັດ:

Hiring labour, as it was the most costly component.

5.1 ອາກາດ

5.2 ພູມິປະເທດ

ໃຫ້ລະບຸ ເຕັກໂນໂລຢີ ທີ່ໄດ້ຖືກນຳໃຊ້:

• ບໍ່ກ່ຽວຂ້ອງ

5.3 ດິນ

ຖ້າເປັນໄປໄດ້ ແມ່ນໃຫ້ຕິດຄັດ ການພັນລະນາດິນ ຫຼື ຂໍ້ມູນສະເພາະຂອງດິນ, ຕົວຢ່າງ, ຄຸນລັກສະນະ ປະເພດຂອງດິນ, ຄ່າຄວາມເປັນກົດ / ເປັນດ່າງຂອງດິນ, ສານອາຫານ,​ ດິນເຄັມ ແລະ ອື່ນໆ.

pH ~7-8.5; SOC 4.7 g/kg of soil; Na ~0.1-0.4 cmolc/kg

5.4 ມີນໍ້າ ແລະ ຄຸນນະພາບ

ມີບັນຫາ ກ່ຽວກັບນໍ້າເຄັມບໍ່?

ບໍ່ແມ່ນ

ເກີດມີນໍ້າຖ້ວມ ໃນພື້ນທີ່ບໍ່?

ບໍ່ແມ່ນ

5.5 ຊີວະນາໆພັນ

ຄວາມຄິດເຫັນ ແລະ ລັກສະນະສະເພາະ ເພີ່ມເຕີມກ່ຽວກັບ ຊີວະນາໆພັນ:

Rangelands in Kenya are generally characterized by high bio-diversity. The particular sites have been degraded in terms of vegetation ans soils. After the restoration diversity increases but has not reached its full potential.

5.6 ຄຸນລັກສະນະ ຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ ທີ່ໄດ້ນໍາໃຊ້ເຕັກໂນໂລຢີ

ໃຫ້ລະບຸ ຄຸນລັກສະນະ ຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ:

Kalama Conservancy receives considerable income from the high end tourism (~60% of total income) and donations (~25% of total income).

5.7 ພື້ນທີ່ສະເລ່ຍຂອງທີ່ດິນ ຫຼື ເຊົ່າໂດຍຜູ້ໃຊ້ທີ່ດິນການນໍາໃຊ້ ເຕັກໂນໂລຢີ

5.8 ເຈົ້າຂອງທີ່ດິນ, ສິດໃຊ້ທີ່ດິນ, ແລະ ສິດທິການນໍາໃຊ້ນໍ້າ

ເຈົ້າຂອງດິນ:

• ຊຸມຊົນ / ບ້ານ

ສິດທິ ໃນການນໍາໃຊ້ທີ່ດິນ:

• ຊຸມຊົນ (ທີ່ມີການຈັດຕັ້ງ)

ສິດທິ ໃນການນໍາໃຊ້ນໍ້າ:

• ຊຸມຊົນ (ທີ່ມີການຈັດຕັ້ງ)

5.9 ການເຂົ້າເຖິງການບໍລິການ ແລະ ພື້ນຖານໂຄງລ່າງ

6.1 ການສະແດງຜົນກະທົບ ພາຍໃນພື້ນທີ່ ທີ່ໄດ້ຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ

ຜົນກະທົບທາງເສດຖະກິດສັງຄົມ

ການຜະລິດ

ຜົນກະທົບດ້ານວັດທະນາທໍາສັງຄົມ

ຜົນກະທົບຕໍ່ລະບົບນິເວດ

ວົງຈອນນໍ້າ / ນໍ້າ

ດິນ

ຊີວະນານາພັນ: ສັດ, ພືດ

6.2 ຜົນກະທົບທາງອ້ອມ ຈາກການນໍາໃຊ້ເຕັກໂນໂລຢີ

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

ການປ່ຽນແປງດິນຟ້າອາກາດ ເທື່ອລະກ້າວ

ການປ່ຽນແປງດິນຟ້າອາກາດ ເທື່ອລະກ້າວ

	ລະດູການ	ຮູບແບບ ການປ່ຽນແປງດິນຟ້າອາກາດ / ທີ່ຮ້າຍແຮງ	ການນໍາໃຊ້ ເຕັກໂນໂລຢີ ສາມາດ ຮັບມື ໄດ້ຄືແນວໃດ?
ອຸນຫະພູມປະຈໍາປີ		ເພີ່ມຂື້ນ	ປານກາງ

ອາກາດ ທີ່ກ່ຽວພັນກັບຄວາມຮຸນແຮງ (ໄພພິບັດທາງທໍາມະຊາດ)

ໄພພິບັດທາງອຸຕຸນິຍົມ

	ການນໍາໃຊ້ ເຕັກໂນໂລຢີ ສາມາດ ຮັບມື ໄດ້ຄືແນວໃດ?
ພະຍຸຝົນ	ດີຫຼາຍ

ໄພພິບັດທາງພູມອາກາດ

	ການນໍາໃຊ້ ເຕັກໂນໂລຢີ ສາມາດ ຮັບມື ໄດ້ຄືແນວໃດ?
ແຫ້ງແລ້ງ	ດີ

6.4 ການວິເຄາະຕົ້ນທຶນ ແລະ ຜົນປະໂຫຍດ

ຈະເຮັດປະໂຫຍດເພື່ອປຽບທຽບກັບຄ່າໃຊ້ຈ່າຍກັບສິ່ງກໍ່ສ້າງ (ຈາກທັດສະນະຂອງຜູ້ນຳໃຊ້ທີ່ດິນ) ໄດ້ແນວໃດ?

6.5 ການປັບຕົວຮັບເອົາເຕັກໂນໂລຢີ

• ກໍລະນີດຽວ / ການທົດລອງ

ທັງໝົດນັ້ນ ແມ່ນໃຜ ທີ່ເປັນຜູ້ປັບຕົວ 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
Land that was previously considered unproductive is now considered grazing land.
Increased infiltration and decreased runoff and water erosion.
Recolonisation by local grasses and forbs to replace reseeded Cenchrus ciliaris after 1-2 years provides nutritious forage (particularly the forbs) for livestock.

ຈຸດແຂງ / ຈຸດດີ / ໂອກາດ ຈາກທັດສະນະຂອງຜູ້ປ້ອນຂໍ້ມູນ ຫຼື ບຸກຄົນສຳຄັນ
Decreased impact of the invasive Acacia reficiens on vegetation and soil within treated areas.
Increased biomass of herbaceous vegetation for livestock and wildlife forage.
Augmented biodiversity after reseeded Cenchrus ciliaris replaced by local grasses and forbs.

6.8 ຈຸດອ່ອນ / ຂໍ້ເສຍ / ຄວາມສ່ຽງ ໃນການນໍາໃຊ້ ເຕັກໂນໂລຢີ ແລະ ວິທີການແກ້ໄຂບັນຫາ

ຈຸດອ່ອນ / ຂໍ້ເສຍ / ຄວາມສ່ຽງໃນມຸມມອງຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ	ມີວິທີການແກ້ໄຂຄືແນວໃດ?
Creates overly high expectations from the community regarding the potential to restore larger areas.	Raise awareness among community members regarding the limitations of large-scale restoration.
Lack of funds to pay labourers. Paying community members to undertake restoration activities rather than these activities being voluntary is now, in hindsight, perceived to have been a mistake.	There will never be enough funding as labourers will continue to expect ever-increasing wages. However, over time, community members may decide to restore land voluntarily. Explore the potential for marketing the main trunks for charcoal production of firewood to pay for the labourers.
Controlling grazing in recovering areas.	Raise awareness about the restoration projects within immediate and neighbouring communities. Also, ensure grazing by-laws are implemented and offenders fined.
Land users unwilling to voluntarily take part in restoration activities.	Increase ownership by conducting restoration projects at more local zonal-levels rather than at the conservancy-level. Create additional incentives by using and marketing of some of the wood material (for legal charcoal production)

ຈຸດອ່ອນ/ຂໍ້ບົກຜ່ອງ/ຄວາມສ່ຽງ ຈາກທັດສະນະຂອງຜູ້ປ້ອນຂໍ້ມູນ ຫຼື ບຸກຄົນສຳຄັນ	ມີວິທີການແກ້ໄຂຄືແນວໃດ?
Inability to provide adequate rest to treated areas (i.e. by controlling grazing pressure) leading to unsuccessful establishment of Cenchrus ciliaris or other herbaceous vegetation in treated areas, particularly in 'buffer zone'.	Implement grazing rules more stringently.
Lack of capacity regarding how to reseed Cenchrus ciliaris in some treated areas. In one case, seeds were buried (as farmers do with maize seeds), which is reported to have contributed to low establishment success of C. ciliaris seeds.	Capacity building.
Germination and establishment of Cenchrus ciliaris depends on timing in relation to the onset of rains, which are unpredictable and led to unsuccessful rehabilitation of some treated areas.	Provide most accurate weather forecasts available.

7.1 ວິທີການ / ແຫຼ່ງຂໍ້ມູນ

7.2 ເອກກະສານອ້າງອີງທີ່ເປັນບົດລາຍງານ

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

'Northern Rangeland Trust: Baseline assessment of rangeland health - Kalama and Namunyak conservancies', Tor-G. Vågen & Leigh A. Winowiecki, 2014

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

https://cgspace.cgiar.org/bitstream/handle/10568/65671/nrtReport_march2014.pdf?sequence=1

7.3 ສາມາດເຊື່ອມໂຍງ ຂໍ້ມູນຂ່າວສານ ໄດ້ໂດຍຜ່ານການອອນລາຍ

ຫົວຂໍ້ / ພັນລະນາ:

Northern Rangeland Trust: Baseline assessment of rangeland health - Kalama and Namunyak conservancies

URL:

https://cgspace.cgiar.org/bitstream/handle/10568/65671/nrtReport_march2014.pdf?sequence=1