1.2 ລາຍລະອຽດ ການຕິດຕໍ່ ຂອງບຸກຄົນທີ່ຊັບພະຍາກອນ ແລະ ສະຖາບັນ ການມີສ່ວນຮ່ວມ ໃນການປະເມີນຜົນ ແລະ ເອກະສານ ຂອງວິທີທາງ

ຊື່ຂອງ ສະຖາບັນການຈັດຕັ້ງ ທີ່ອໍານວຍຄວາມສະດວກ ໃນການສ້າງເອກກະສານ ຫຼື ປະເມີນແນວທາງ (ຖ້າກ່ຽວຂ້ອງ)

University of Reading (University of Reading) - ລາຊະອານາຈັກອັງກິດ

1.3 ເງື່ອນໄຂ ຂອງການນໍາໃຊ້ເອກກະສານຂໍ້ມູນ ຂອງ WOCAT

ເມື່ອໃດທີ່ໄດ້ສັງລວມຂໍ້ມູນ (ຢູ່ພາກສະໜາມ)?

03/05/2016

ຜູ້ສັງລວມ ແລະ ບັນດາຜູ້ຕອບແບບສອບຖາມ ຍອມຮັບໃນເງື່ອນໄຂ ການນໍາໃຊ້ຂໍ້ມູນເອກະສານ ທີ່ສ້າງຂື້ນ ໂດຍຜ່ານ ອົງການ WOCAT:

ແມ່ນ

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

2.1 ການອະທິບາຍ ໂດຍຫຍໍ້ ຂອງວິທີທາງ

Acidification treatments were applied to improved pastures in an attempt to restore plots to low-intensity grazing land

2.2 ການອະທິບາຍ ລາຍລະອຽດ ຂອງວິທີທາງ

ການອະທິບາຍ ລາຍລະອຽດ ຂອງວິທີທາງ:

Aims / objectives: To convert the area from intensive pastureland to a semi-natural state with low intensity grazing through alteration of the soil pH. This change in land-use should have a positive effect on both above- and belowground biodiversity.

Methods: Plots were established on two adjacent farms owned by National Trust near Wareham, Dorset (Newlines Farm and Hartland Farm). A control and two sulphur amendments were compared on plots on ten fields (five from each farm) on 50 m x 50 m plots. Elemental sulphur (Brimestone 90TM) or ferrous sulphate (Mistrale “Wet Copperas” 50TM) were applied at equal rates of 2000 kg ha-1 in May 2000 and a second application of 1600 kg ha-1 in March 2001.

Stages of implementation: Treatments were applied in 2000 and 2001. Periodic monitoring has been conducted to monitor changes in plant diversity and soil chemical and biological properties.

Role of stakeholders: Stakesholders played an active role in identifying management options and implementing the technology. When the original plots were established, a charitable organisation was the primary stakeholder. For the intent of the current project, other stakeholders became involved, including parish council, landowners, and conservation organisations.

Other important information: Acidification treatments were applied to plots on the Isle of Purbeck that had previously been used for arable production and then high intensity grazing. The site is located on acidic fluvially-deposited soil and was in lowland heath until the middle of the 20th century at which time the land was tilled and treatments of rock phosphate, marl and chalk were added to increase soil pH and nutrient availability and improve the potential of the land for agricultural production.

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

The Approach focused mainly on other activities than SLM (soil, pH, below-ground biodiversity, low-intensity grazing)

To manage soil pH change and associated effects on above and below-ground diversity and function

The SLM Approach addressed the following problems: Management of soil pH and land use change to less intensive system

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	ການຊ່ວຍເຫຼືອຈາກພາຍນອກ	Land owners who acquired national support
ການວາງແຜນ	ການຊ່ວຍເຫຼືອຈາກພາຍນອກ	By specialist
ການປະຕິບັດ	ການຮ່ວມມື	By land owner and specialist
ຕິດຕາມກວດກາ / ການປະເມີນຜົນ	ການຊ່ວຍເຫຼືອຈາກພາຍນອກ	By Specialist
Research	ການຊ່ວຍເຫຼືອຈາກພາຍນອກ	By specialist

3.4 ການຕັດສິນໃຈກ່ຽວກັບການຄັດເລືອກເຕັກໂນໂລຢີຂອງການຄຸ້ມຄອງທີ່ດິນແບບຍືນຍົງ / ເຕັກໂນໂລຢີ

ລະບຸ ຄົນທີ່ຕັດສິນໃຈ ກ່ຽວກັບການຄັດເລືອກຂອງ ເຕັກໂນໂລຢີ / ເຕັກໂນໂລຢີ ຈະໄດ້ຮັບການປະຕິບັດ:

• ຜູ້ຊ່ຽວຊານ ຫຼັກດ້ານການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ, ມີການຕິດຕາມປຶກສາຫາລືກັບຜູ້ນໍາໃຊ້ທີ່ດິນ

ອະທິບາຍ:

Decisions on the method of implementing the SLM Technology were made by mainly by land users supported by SLM specialists

4.1 ການສ້າງຄວາມສາມາດ / ການຝຶກອົບຮົມ

ຜູ້ນໍາໃຊ້ທີ່ດິນ ຫຼື ພາກສ່ວນກ່ຽວຂ້ອງອື່ນໆ ໄດ້ຮັບການຝຶກອົບຮົມບໍ່?

ແມ່ນ

ໃຫ້ລະບຸ ຜູ້ໃດທີ່ໄດ້ຮັບການຝຶກອົບຮົມ:

• ຜູ້ນໍາໃຊ້ດິນ
• ພະນັກງານພາກສະໜາມ / ທີ່ປຶກສາ

ຮູບແບບຂອງການຝຶກອົບຮົມ:

• ຕົວຕໍ່ຕົວ
• ກອງປະຊຸມ

4.2 ການບໍລິການໃຫ້ຄໍາປຶກສາ

ເຮັດຜູ້ໃຊ້ທີ່ດິນມີການເຂົ້າເຖິງການບໍລິການໃຫ້ຄໍາປຶກສາ?

ແມ່ນ

ລະບຸວ່າການສະໜອງ ການບໍລິການ ໃຫ້ຄໍາປຶກສາ:

• ໃນພື້ນທີ່ຂອງຜູ້ນໍາໃຊ້ດິນ

• Public meetings

ອະທິບາຍ / ຄວາມຄິດເຫັນ:

Advisory service was not foreseen for this approach

Advisory service is totally inadequate to ensure the continuation of land conservation activities; No additional government funding has been acquired.

4.3 ສະຖາບັນການສ້າງຄວາມເຂັ້ມແຂງ (ການພັດທະນາອົງການຈັດຕັ້ງ)

ສະຖາບັນ ໄດ້ຮັບການສ້າງຕັ້ງຂື້ນ ຫຼື ໄດ້ຮັບການສ້າງຄວາມເຂັ້ມແຂງ ໂດຍການຈັດຕັ້ງປະຕິບັດ ວິທີທາງບໍ່?

• ບໍ່ມີ

4.4 ຕິດຕາມກວດກາ ແລະ ປະເມີນຜົນ

ການຈັດຕັ້ງປະຕິບັດ ວິທີທາງ ໄດ້ມີການປະເມີນຜົນ ແລະ ຕິດຕາມບໍ?

ແມ່ນ

ຄວາມຄິດເຫັນ:

bio-physical aspects were regular monitored by project staff through observations

bio-physical aspects were regular monitored by project staff through measurements

technical aspects were regular monitored by project staff through observations

technical aspects were regular monitored by project staff through measurements

area treated aspects were regular monitored through observations

area treated aspects were regular monitored through measurements

There were no changes in the Approach as a result of monitoring and evaluation

There were no changes in the Technology as a result of monitoring and evaluation

4.5 ການຄົ້ນຄວ້າ

ນີ້້ແມ່ນສ່ວນໜຶ່ງ ການຄົ້ນຄວ້າ ຂອງວິທີທາງບໍ່?

ແມ່ນ

ລະບຸ ຫົວຂໍ້:

• ລະບົບນິເວດ
• ເຕັກໂນໂລຢີ

ໃຫ້ຂໍ້ມູນ ເພີ່ມເຕີມ ແລະ ກໍານົດ ຜູ້ໃດເຮັດການຄົ້ນຄວ້າ:

Research on the approach has been carried out by specialists at Bournemouth University and the University of Reading, UK.

Research was carried out on-farm

5.1 ງົບປະມານປະຈໍາປີ ສໍາລັບວິທີທາງ ຂອງການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ

ຖ້າຫາກບໍ່ຮູ້ຈັດງົບປະມານທີ່ແນ່ນອນ ແມ່ນໃຫ້ປະມານເອົາ:

• 10,000-100,000

ຄໍາເຫັນ (ຕົວຢ່າງ: ແຫຼ່ງຂໍ້ມູນຫຼັກ ຂອງການສະໜອງທຶນ / ຜູ້ໃຫ້ທຶນທີ່ສໍາຄັນ):

Approach costs were met by the following donors: government (Department of Environment, Food & Rural Affairs): 50.0%; national non-government (National Trust): 30.0%; other (University): 20.0%

5.2 ການສະໜັບສະໜູນ ທາງດ້ານການເງິນ / ອຸປະກອນ ສະໜອງໃຫ້ແກ່ຜູ້ນໍາທີ່ດິນ

ຜູ້ນໍາໃຊ້ດິນ ໄດ້ຮັບການສະໜັບສະໜູນ ທາງດ້ານ ການເງິນ / ອຸປະກອນ ໃນການຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີບໍ?

ແມ່ນ

5.3 ເງິນສົມທົບສໍາລັບການນໍາໃຊ້ສະເພາະປັດໃຈຂາເຂົ້າໃນການຜະລີດກະສິກໍາ (ລວມທັງແຮງງານ)

• ກະສິກໍາ

ຖ້າແຮງງານ ຂອງຜູ້ນໍາໃຊ້ດິນ ໄດ້ຮັບການສະໜັບສະໜູນ ປັດໃຈຂາເຂົ້າ, ແມ່ນບໍ່:

• ການອາສາ

5.4 ສິນເຊື່ອ

ໄດ້ປ່ອຍສິນເຊື່ອ ສະໜອງໃຫ້ພາຍໃຕ້ ວິທີການສໍາລັບກິດຈະກໍາ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນນຍົງບໍ່?

ບໍ່ແມ່ນ

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
Decreased spending on inputs where the only input in the system in dung from cattle grazing (How to sustain/ enhance this strength: Continue grazing at a low enough density to allow adequate plant regrow)
Decreased labour required for management
Decreased compaction since regular use of tractors on site is no longer required (How to sustain/ enhance this strength: Attempt to minimizing compaction by grazing livestock)

ຈຸດແຂງ / ຈຸດດີ / ໂອກາດ ຈາກທັດສະນະຂອງຜູ້ປ້ອນຂໍ້ມູນ ຫຼື ບຸກຄົນສຳຄັນ
The conversion in land use from a improved agriculture to a semi- natural low input grazing system should have a positive effect on above- and belowground biodiversity.
Considering that the Isle of Purbeck was historically a region of cultural importance, returning the system to a more natural state has important implications for the cultural and recreational value of the land.
Low input systems can increase resilience of the system to global change

6.5 ຈຸດອ່ອນ / ຂໍ້ເສຍຂອງແນວທາງ ແລະ ວິທີການແກ້ໄຂໃຫ້ເຂົາເຈົ້າ

ຈຸດອ່ອນ / ຂໍ້ເສຍ / ຄວາມສ່ຽງໃນມູມມອງຂອງຜູ້ນໍາໃຊ້ທີ່ດິນ	ມີວິທີການແກ້ໄຂຄືແນວໃດ?
Fertilizer application rate too high for one application	Smaller, regular additions over several years
Decrease in economic returns
Shrub encroachment (i.e. gorse; Alex europaeus) can be a problem when converting to low input pasture land in this region.	Grazing, mowing, and chemical herbicides are some options for slowing invasions.

ຈຸດອ່ອນ ຫຼື ຂໍ້ເສຍ ຫຼື ຄວາມສ່ຽງ ໃນມຸມມອງຂອງ ຜູ້ສັງລວມຂໍ້ມູນ ຫຼື ບັນດາຜູ້ຕອບແບບສອບຖາມ	ມີວິທີການແກ້ໄຂຄືແນວໃດ?
Over time nutrients are being drawn down but exporting meat off the land with no inputs	Periodic applications of nutrients may be required to ensure long-term fertility of the system
Land use change and restoration are slow process and may result in economic losses on managed lands

7.1 ວິທີການ / ແຫຼ່ງຂໍ້ມູນ

7.2 ເອກະສານທົ່ວໄປທີ່ສາມາດໃຊ້ໄດ້

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

Re-creation of heathland on improved pasture using top soil removal and sulphur amendments: Edaphic drivers and impacts of ericoid mycorrhizas, Diaz, A., Green, I., Tibbett, M., 2008Heathland restoration on former agricultural land: Effects of artificial acidification on the availability and uptake of toxic metal cation, Green, I., Stockdale, J., Tibbett, M., Diaz, I., 2007Are sulphurous amendments an effective tool in the restoration of heathland and acidic grassland after four decades of rock phosphate fertlization, Tibbett, M., Diaz, A., 2005The restoration of heathland and acid grassland at Hartland and Newline Farms, Tibbett, M., Diaz, A., 2001

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

Biological Conservation, 141:1628-1635, http://www.sciencedirect.com/science/article/pii/S0006320708001353Water Air Soil Pollution, 178:287-295, http://link.springer.com/article/10.1007/s11270-006-9197-8Restoration Ecology, 13:83-91, http://onlinelibrary.wiley.com/doi/10.1111/j.1526-100X.2005.00010.x/epdfFirst Year Report to National Trust, Purbeck

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

Heathland restoration on former agricultural land: Effects of artificial acidification on the availability and uptake of toxic metal cation, Green, I., Stockdale, J., Tibbett, M., Diaz, I., 2007

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

Water Air Soil Pollution, 178:287-295, http://link.springer.com/article/10.1007/s11270-006-9197-8

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

Are sulphurous amendments an effective tool in the restoration of heathland and acidic grassland after four decades of rock phosphate fertlization, Tibbett, M., Diaz, A., 2005

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

Restoration Ecology, 13:83-91, http://onlinelibrary.wiley.com/doi/10.1111/j.1526-100X.2005.00010.x/epdf

ຫົວຂໍ້, ຜູ້ຂຽນ, ປີ, ISBN:

The restoration of heathland and acid grassland at Hartland and Newline Farms, Tibbett, M., Diaz, A., 2001

ມີຢູ່ໃສ?ມູນຄ່າເທົ່າໃດ?

First Year Report to National Trust, Purbeck