1.2 ຂໍ້ມູນ ການຕິດຕໍ່ພົວພັນ ຂອງບຸກຄົນທີ່ສໍາຄັນ ແລະ ສະຖາບັນ ທີ່ມີສ່ວນຮ່ວມ ໃນການປະເມີນເອກກະສານ ເຕັກໂນໂລຢີ

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

2.1 ຄໍາອະທິບາຍສັ້ນຂອງ ເຕັກໂນໂລຢີ

ການກຳໜົດຄວາມໝາຍ ຂອງເຕັກໂນໂລຢີ:

Lolldaiga Hills ranch is a private ranch and conservancy with livestock production and tourism. Rotational grazing is used to manage livestock on semi-arid lands with limited water resources. Bare land is recovered by a "Boma” technology – strategic corralling of animals overnight on degraded land.

2.2 ການອະທິບາຍ ລາຍລະອຽດ ຂອງເຕັກໂນໂລຢີ

ການພັນລະນາ:

Livestock production on Lolldaiga Hills ranch is managed under an extensive grazing system for dairy, beef, sheep and camel production, with strategic fattening and selling, in harmony with conservation principles. The conservancy is dedicated to the sustainable conservation of critical habitat and wildlife. The ranch serves also as a training ground for the British Army.
Grazing is managed without fixed blocks. Grazing areas vary considerably, depending on rainfall and location within the farm. Similarly, grazing duration in one area also varies significantly (from two weeks to eight months). Starting after the long rains (April to May), livestock are moved gradually from north to south: movement only occurs when areas are completely grazed. They stay for about four months in the north and eight months in the south - due to better grass in the southern part. Some of the dry season grazing is land set aside for later use. They use, for instance, highland forests in the west where zebra and other livestock are largely absent. During the rains, grazing takes place on a much smaller area than during the dry season, where water can be a major challenge. Livestock are kept together, though steers/heifers/breeding cows/resting bulls are separated into different herds of 90-150 units per herd. But these are not tightly “bunched” as in other ranches in the area which apply “Holistic Management” principles, since bunching is not appropriate due to strong wind erosion. The closer livestock are aggregated, the more damage – that is dust generated - in dry areas. As is typical of private ranches in Laikipia, Lolldaiga supports some of the highest densities of wildlife in Kenya. The wild herbivore biomass density on private ranches is estimated by Georgiadis (2007) at 14 ha /TLU.

Whilst the livestock is moving, large bomas (corrals in Kiswahili) are constructed for the herds. Here, animals are closely together kept in protective enclosures overnight. Bomas are strategically sited on bare areas to recover the land through dung accumulation and breaking soil crusts by hooves. Currently, there are 20 bomas covering an area of 0.02 km2 (0.01% of their land). This can be taken to represent the area that can be restored each year. Boma sites are steadily but slightly shifted. On average, one boma is located on the same denuded patch for only one to two weeks during the dry season, and again for one week during the wet season.
In a single boma of 0.1 ha, 400 cows are corralled. Former bare patches with bomas have recovered well after just a few years. Results of a boma site comparison (see Herger 2018) have shown how bomas turn into ecological hotspots with a long-lasting effect. Amounts of soil organic carbon (SOC), as well as macro- and micronutrients in topsoil (especially) and subsoil of former boma sites were much higher than reference sites close-by. The chronology of former boma sites (1, 5, 9 years ago) also played a decisive role in soil parameters. Former boma sites from 5 and 9 years ago performed better than the most recent boma (1 year ago).

On the ranch, due to lack of rains, fodder supplements had to be purchased in 2016. However, it is usually water and not grazing that is the limiting factor on the rangeland.
Whereas cattle are sold to the leading meat producer "Farmer's Choice" (80% for domestic distribution, 20% for export to neighbouring countries and the Middle East), sheep are sold to East African Seafood (Nairobi) and camels to Somalis in town and local butcheries.
Lolldaiga also assists community grazing. The ranch helps neighbouring group ranches by allowing them access to their land for fattening purposes, but mostly as a grass bank during droughts (sometimes charging a small fee, sometimes none). During dry spells, they host on average 500-1000 heads from other communities. Along their fence informal (strictly "illegal") grazing of goats and sheep is tolerated.

2.3 ຮູບພາບຂອງເຕັກໂນໂລຢີ

2.5 ປະເທດ / ເຂດ / ສະຖານທີ່ບ່ອນທີ່ ເຕັກໂນໂລຢີ ໄດ້ຮັບການນໍາໃຊ້ ແລະ ທີ່ຖືກປົກຄຸມດ້ວຍການປະເມີນຜົນ

ປະເທດ:

ເຄັນຢາ

ພາກພື້ນ / ລັດ / ແຂວງ:

Laikipia

ໃຫ້ລະບຸ ການແຜ່ຂະຫຍາຍ ເຕັກໂນໂລຢີ:

• ແຜ່ຂະຫຍາຍຢ່າງໄວວາໃນພື້ນທີ່

ຖ້າຫາກວ່າເຕັກໂນໂລຢີ ໄດ້ກະຈາຍໄປທົ່ວພື້ນທີ່, ໃຫ້ລະບຸເນື້ອທີ່ ທີ່ຖືກປົກຄຸມ (ເປັນ ກິໂລຕາແມັດ):

200.0

ຖ້າຫາກບໍ່ຮູ້ເນື້ອທີ່ທີ່ແນ່ນອນ, ໃຫ້ລະບຸ ເນື້ອທີ່ໂດຍປະມານ ທີ່ໃກ້ຄຽງ:

• 100-1,000 ກມ 2

ຄວາມຄິດເຫັນ:

Lolldaiga has an area size of 200 km2. Similar technologies are also applied on other ranches (see the documentations for "Il Ngwesi", "Makurian", and "Borana")

Map

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2.6 ວັນທີໃນການຈັດຕັ້ງປະຕິບັດ

ຖ້າຫາກວ່າ ບໍ່ຮູ້ຈັກ ປີທີ່ຊັດເຈນ ແມ່ນໃຫ້ປະມານ ວັນທີເອົາ:

• 10-50 ປີ ຜ່ານມາ

2.7 ການນໍາສະເໜີ ເຕັກໂນໂລຢີ

ໃຫ້ລະບຸ ເຕັກໂນໂລຢີ ໄດ້ຖືກຈັດຕັ້ງປະຕິບັດຄືແນວໃດ?

• ໂດຍຜ່ານນະວັດຕະກໍາຄິດຄົ້ນຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ

3.1 ຈຸດປະສົງຫຼັກ (ຫຼາຍ) ຂອງເຕັກໂນໂລຢີ

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

3.2 ປະເພດການນໍາໃຊ້ທີ່ດິນ ໃນປະຈຸບັນ() ທີ່ເຕັກໂນໂລຢີ ໄດ້ຖືກນໍາໃຊ້

ທົ່ງຫຍ້າລ້ຽງສັດ

ການລ້ຽງສັດແບບປ່ອຍ ຕາມທຳມະຊາດ:

• ແບບຂັງຄອກ

ປະເພດສັດ:

• ອູດ
• ແກະ

• cattle

ຜະລິດຕະພັນ ແລະ ການບໍລິການ:

• ຊີ້ນ
• ນ້ຳນົມ
• ຂົນສັດ

ສາຍພັນ:

ແກະ

ນັບ:

1800

ສາຍພັນ:

ອູດ

ນັບ:

140

ການຕັ້ງຖິ່ນຖານ, ພື້ນຖານໂຄງລ່າງ

• ການຕັ້ງຖິ່ນຖານ, ອາຄານ

ຂໍ້ສັງເກດ:

Few facilities for tourism.
Few farm houses.

ຄວາມຄິດເຫັນ:

Grassed acacia bushland. Overall rather good vegetation coverage with some patches of bare ground. Especially in the northern part Lolldaiga is effected by the invasive species "Opuntia stricta". Dominant grasses: Pennisetum species, Eragrostis species, Cynadon species, Hyparrhenia species, Kelenger species. Dominant shrubs: Solyneum inconum, Lyceum europaeum, Barleria acuthodies, Grewia tembensis, Opuntia. Dominant trees: Acacia etbaica, Acacia drepanalobium, Acacia mellifera. Detailed list of all species (vegetation and wildlife) available (Herger 2018)

Main animal species and products: Cattle, sheep, camels; Milk, wool, beef, camel meat, and lamb/ mutton. High-quality segment. Domestic (80%, Nairobi and hotels), international distribution (20%, neighbouring countries and the Middle East) Livestock: 3,920 TLU; Stocking rate: 5.1 ha/TLU Pressure on land including wildlife numbers (estimated by Georgiadis 2007): 3.7 ha/TLU Livestock numbers: 5,200 cattle, 1,800 sheep, 140 camels Sales: Cattle 20% sales, Sheep 15%, Camels 10%. Additional 1,000-2,000 livestock units from neighbouring community farms during droughts. Goats and sheep illegally grazing along the fence are tolerated. Wildlife: Giraffe, antelope/gazelle (e.g. gerenuk, impala, Thomson's gazelle), baboons, zebra, dikdik, hares, elephant and others. More wildlife than on group ranches. Wildlife herbivore biomass density (Georgiadis 2007) 14 ha/TLU

Number of growing seasons per year: 2
Short rains in November and December. Long rains in April and May. Rains from (October) November to December are usually better in this area. Rainfalls with strong local variations and changing regimes.
Livestock density: 3'920 TLU; Stocking rate: 5.1 ha/TLU, Pressure on land including wildlife numbers (estimated by Georgiadis 2007): 3.7 ha/TLU

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 ທາງດ້ານການຄຸ້ມຄອງ

• M2: ການປ່ຽນແປງ ການຈັດການຄຸ້ມຄອງ / ລະດັບຄວາມໜາແໜ້ນ
• M4: ການປ່ຽນແປງ ໄລຍະເວລາ ໃນການຈັດຕັ້ງປະຕິບັດ ກິດຈະກໍາ

3.7 ປະເພດດິນເຊື່ອມໂຊມ ຫຼັກທີ່ໄດ້ນໍາໃຊ້ ເຕັກໂນໂລຢີ

ດິນເຊາະເຈື່ອນ ໂດຍນໍ້າ

• Wt: ການສູນເສຍຊັ້ນໜ້າດິນ / ການເຊາະເຈື່ອນຜິວໜ້າດິນ
• Wg: ການເຊາະເຈື່ອນຮ່ອງນ້ຳ / ຫ້ວຍ

ດິນເຊາະເຈື່ອນ ໂດຍລົມ

• ການສູນເສຍຊັ້ນໜ້າດິນ

ການເຊື່ອມໂຊມ ຂອງດິນ ທາງກາຍະພາບ

• Pc: ການອັດແໜ້ນ
• Pk: ການບັນເທົາ ແລະ ການປົກຄຸມຂອງເປືອກໂລກ
• Pi: ເນື້ອດິນ ທີ່ມີຂະໜາດນ້ອຍຫຼາຍ

ການເຊື່ອມໂຊມ ທາງຊີວະພາບ

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

ຄວາມຄິດເຫັນ:

Across the grasslands and rangelands, an increase in bare land and bush has been a clear trend all over Laikipia for many years, both on community-owned lands and private ranches. Major identified ecological problems (partly) caused by livestock production are: bare ground, low contents of soil organic carbon and plant-available nutrients, soil erosion (sealing, crusting, rills and gullies, water flow patterns, sheet erosion, pedestals), poor soil properties, undesirable species, and (increasing) woody and invasive species. The current major problem on rangelands is the invasive species Opuntia stricta, which however only could spread that widely because of degraded land in the first place. The technology aims at improving vegetation cover of the land and thereby reducing further degradation and restoring degraded land. However, Lolldaiga is clearly not as much affected by degradation (compare Herger 2018).

3.8 ການປ້ອງກັນ, ການຫຼຸດຜ່ອນ, ຫຼືການຟື້ນຟູຂອງການເຊື່ອມໂຊມຂອງດິນ

ໃຫ້ລະບຸ ເປົ້າໝາຍ ເຕັກໂນໂລຢີ ທີ່ພົວພັນ ກັບຄວາມເຊື່ອມໂຊມຂອງດິນ:

• ຫຼຸດຜ່ອນການເຊື່ອມໂຊມຂອງດິນ
• ການຟື້ນຟູ / ຟື້ນຟູດິນທີ່ຊຸດໂຊມ

4.1 ເຕັກນິກ ໃນການແຕ້ມແຜນວາດ ເຕັກໂນໂລຢີ

ຜູ້ຂຽນ:

Michael Herger

ວັນທີ:

16/01/2018

4.2 ຂໍ້ມູນທົ່ວໄປກ່ຽວກັບການຄິດໄລ່ປັດໃຈຂາເຂົ້າໃນການຜະລິດ ແລະ ມູນຄ່າອື່ນໆ

ລະບຸ ວິທີການ ຄຳໃຊ້ຈ່າຍ ແລະ ປັດໄຈນໍາເຂົ້າ ທີ່ໄດ້ຄິດໄລ່:

• ຕໍ່ຫົວໜ່ວຍ ທີ່ໄດ້ຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ

ລະບຸ ສະກຸນເງິນທີ່ໃຊ້ສໍາລັບ ການຄິດໄລ່ຄ່າໃຊ້ຈ່າຍ:

• USA

4.5 ບໍາລຸງຮັກສາ / ແຜນຈັດຕັ້ງປະຕິບັດ ກິດຈະກໍາ

4.6 ຄ່າໃຊ້ຈ່າຍ ແລະ ປັດໄຈນໍາເຂົ້າທີ່ຈໍາເປັນສໍາລັບການບໍາລຸງຮັກສາກິດຈະກໍາ / ແຜນປະຕິບັດ (ຕໍ່ປີ)

ຄວາມຄິດເຫັນ:

Animal treatment costs are estimated according to other ranches in the area since figures for Lolldaiga are missing. Figures are not reconfirmed data.

4.7 ປັດໄຈ ທີ່ສໍາຄັນ ທີ່ສົ່ງຜົນກະທົບ ຕໍ່ຄ່າໃຊ້ຈ່າຍ

ໃຫ້ອະທິບາຍ ປັດໃຈ ທີ່ສົ່ງຜົນກະທົບ ຕໍ່ຕົ້ນທຶນ ໃນການຈັດຕັ້ງປະຕິບັດ:

Labor

5.1 ອາກາດ

5.2 ພູມິປະເທດ

5.3 ດິນ

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

SOC 0.9-1.8 %
pH: 6.3
Clay: 9 %
Silt: 47 %
Sand: 44 %
More rangeland health data in Herger (2018)

5.4 ມີນໍ້າ ແລະ ຄຸນນະພາບ

ມີບັນຫາ ກ່ຽວກັບນໍ້າເຄັມບໍ່?

ບໍ່ແມ່ນ

ເກີດມີນໍ້າຖ້ວມ ໃນພື້ນທີ່ບໍ່?

ບໍ່ແມ່ນ

5.5 ຊີວະນາໆພັນ

ຄວາມຄິດເຫັນ ແລະ ລັກສະນະສະເພາະ ເພີ່ມເຕີມກ່ຽວກັບ ຊີວະນາໆພັນ:

Grassed acacia bushland. Overall rather good vegetation coverage with some patches of bare ground. Especially in the northern part Lolldaiga is effected by the invasive species "Opuntia stricta". Dominant grasses: Pennisetum species, Eragrostis species, Cynadon species, Hyparrhenia species, Kelenger species. Dominant shrubs: Solyneum inconum, Lyceum europaeum, Barleria acuthodies, Grewia tembensis, Opuntia. Dominant trees: Acacia etbaica, Acacia drepanalobium, Acacia mellifera. Detailed list of all species (vegetation and wildlife) available (Herger 2018)

5.6 ຄຸນລັກສະນະ ຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ ທີ່ໄດ້ນໍາໃຊ້ເຕັກໂນໂລຢີ

5.7 ເນື້ອທີ່ສະເລ່ຍຂອງດິນ ທີ່ຜູ້ນຳໃຊ້ທີ່ດິນ ໃຊ້ເຮັດເຕັກໂນໂລຢີ

5.8 ເຈົ້າຂອງທີ່ດິນ, ສິດໃຊ້ທີ່ດິນ, ແລະ ສິດທິການນໍາໃຊ້ນໍ້າ

ເຈົ້າຂອງດິນ:

• ບຸກຄົນ, ທີ່ມີຕໍາແໜ່ງ

ສິດທິ ໃນການນໍາໃຊ້ທີ່ດິນ:

• ບຸກຄົນ

ສິດທິ ໃນການນໍາໃຊ້ນໍ້າ:

• ບຸກຄົນ

ຄວາມຄິດເຫັນ:

Masai in the area have claimed that land leases of white settlers have expired and the land belongs to them. Government states the land belongs to the private ranchers, but the future development is unknown. There have already been conflicts and are likely to happen again. On the other hand, cooperation with group ranches has increased.

5.9 ການເຂົ້າເຖິງການບໍລິການ ແລະ ພື້ນຖານໂຄງລ່າງ

6.5 ການປັບຕົວຮັບເອົາເຕັກໂນໂລຢີ

• ກໍລະນີດຽວ / ການທົດລອງ

ຖ້າຫາກວ່າມີ, ປະລິມານ (ຈໍານວນຂອງຄົວເຮືອນ / ເນື້ອທີ່ການຄຸ້ມຄອງ):

Similar practices, but different. Most ranches implement Holistic Management.

6.6 ການປັບຕົວ

ໄດ້ມີການດັດປັບ ເຕັກໂນໂລຢີ ເພື່ອໃຫ້ແທດເໝາະກັບເງື່ອນໄຂ ການປ່ຽນແປງບໍ?

ບໍ່ແມ່ນ

6.7 ຈຸດແຂງ / ຂໍ້ດີ / ໂອກາດ ໃນການນໍາໃຊ້ ເຕັກໂນໂລຢີ

7.1 ວິທີການ / ແຫຼ່ງຂໍ້ມູນ

7.2 ເອກກະສານອ້າງອີງທີ່ເປັນບົດລາຍງານ

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

Herger, M.B. (2018). Environmental Impacts of Red Meat Production. MSc Thesis. University of Bern.

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

University of Bern

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

Georgiadis, N.J., Olivero, I.N., Romanach, S.S. (2007). Savanna herbivore dynamics in a livestock-dominated landscape: I. Dependence on land use, rainfall, density, and time. Biology Conservation 137(3): 461-472.

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

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