1.2 ព័ត៌មានលម្អិតពីបុគ្គលសំខាន់ៗ និងស្ថាប័នដែលចូលរួមក្នុងការវាយតម្លៃ និងចងក្រងឯកសារនៃបច្ចេកទេស

ឈ្មោះគម្រោងដែលបានចងក្រងឯកសារ/ វាយតម្លៃលើបច្ចេកទេស (បើទាក់ទង)

Programme d’Appui à l’agriculture Productive (GIZ / PROMAP)

ឈ្មោះគម្រោងដែលបានចងក្រងឯកសារ/ វាយតម្លៃលើបច្ចេកទេស (បើទាក់ទង)

Manual of Good Practices in Small Scale Irrigation in the Sahel (GIZ )

ឈ្មោះអង្គភាពមួយ (ច្រើន) ដែលបានចងក្រងឯកសារ/ វាយតម្លៃបច្ចេកទេស (បើទាក់ទង)

Deutsche Gesellschaft für Internationale Zusammenarbeit (GIZ) GmbH (GIZ) - ប្រទេសអាល្លឺម៉ង់

ឈ្មោះអង្គភាពមួយ (ច្រើន) ដែលបានចងក្រងឯកសារ/ វាយតម្លៃបច្ចេកទេស (បើទាក់ទង)

Misereor - ប្រទេសអាល្លឺម៉ង់

1.3 លក្ខខណ្ឌទាក់ទងទៅនឹងការប្រើប្រាស់ទិន្នន័យដែលបានចងក្រងតាមរយៈ វ៉ូខេត

អ្នកចងក្រង និង(បុគ្គលសំខាន់ៗ)យល់ព្រមទទួលយកនូវលក្ខខណ្ឌនានាទាក់ទងទៅនឹងការប្រើប្រាស់ទិន្នន័យដែលបានចងក្រងតាមរយៈវ៉ូខេត:

បាទ/ចា៎

2.1 ការពណ៌នាដោយសង្ខេបពីបច្ចេកទេស

និយមន័យបច្ចេកទេស:

Contour stone bunds are erosion control structures and improve water retention and infiltration into the soil, resulting in an increased harvest.

2.2 ការពណ៌នាលម្អិតពីបច្ចេកទេស

ការពណ៌នា:

Contour stone bunds are erosion control structures built with quarry rock or stones in series of two or three. They are constructed in lines along the natural contour of the land after 10-15 cm of the soil has been removed from the line where they are to be built. They should be built to a height of 20-30 cm from the ground and spaced 20 to 50 m apart depending on the inclination of the terrain.
The best results are achieved when contour stone bunds are used in combination with biological measures (planting of grass, trees and hedges) and the use of organic fertiliser and mulching.

Purpose of the Technology: Contour stone bunds protect the land against sheet erosion caused by runoff. They form a barrier that slows down runoff and spreads it more evenly over the land. By slowing the flow of water over the land, it can seep into the soil and prevents the loss of rainwater. The bunds also act as a filter, trapping fine waterborne particles of soil and manure, resulting in a build-up of sediment and the formation of terraces. The seeds of grasses and shrubs are also trapped by the bunds, favouring the establishment of natural vegetation along the structure. This further stabilises the soil and the bunds and contributes to conserving the biodiversity of plants and small wild animals (monitor lizards, birds, snakes and other reptiles). If good vegetation cover is developed on the stone bunds, they also lower soil temperature and provide protection against wind erosion. Excess water filters through the bunds and infiltrates into the soil. When rainfall is erratic, the stone bunds contribute to conserving more moisture in the soil for longer, which helps to alleviate water stress during dry spells. There is evidence that bunds that have been in place for over 15 years have positive effects on yields.

Establishment / maintenance activities and inputs: A minimum amount of upkeep is required, which essentially involves replacing stones dislodged by animals or water flow. The lifespan of a stone bund is over 20 years.
In order to optimise the positive effects of stone bunds, it is important to ensure that they are constructed closely following the natural contour of the land and in accordance with the established technical standards.
The means of transport required depends on the proximity of a quarry or a supply of stones (cart or lorry).

Natural / human environment: This technique is designed for cropland, but can also be used on forest/rangeland. It is suitable for areas in the Sahel and the Sudan with rainfall ranging between 300 and 900 mm/year and low-to-medium gradient terrain.
When rainfall is high, they protect the land in the event of heavy rain, a phenomenon that tends to increase with climate change.

2.3 ​រូបភាពនៃបច្ចេកទេស

2.5 ប្រទេស/តំបន់/ទីតាំងកន្លែង ដែលបច្ចេកទេសត្រូវបានអនុវត្ត និងបានគ្រប់ដណ្តប់ដោយការវាយតម្លៃនេះ

2.6 កាលបរិច្ឆេទនៃការអនុវត្ត

ប្រសិនបើមិនច្បាស់ឆ្នាំ សូមបញ្ជាក់កាលបរិច្ឆេទដែលប្រហាក់ប្រហែល:

• 10-50 ឆ្នាំ

2.7 ការណែនាំពីបច្ចេកទេស

សូមបញ្ជាក់តើបច្ចេកទេសត្រូវបានណែនាំឱ្យអនុវត្តដោយរបៀបណា:

• តាមរយៈគម្រោង / អន្តរាគមន៍ពីខាងក្រៅ

មតិយោបល់ (ប្រភេទនៃគម្រោង ។ល។):

Known as traditional method in some areas. Improved and up-scaled as part of numerous projects in many semi-arid countries. German Developmenmt Cooperation has used the technology from the 1980s onwards to combat desertification and improve natural resource management e.g. PDRT (Projet de développement rural de Tahoua - Tahoua Rural Development Project), PASP (Projet de protection intégrée des ressources agro-sylvo-pastorales Tillabéri-Nord - Project for the Integrated Protection of Agricultural, Forest and Rangeland Resources in Tillabéri-Nord) and several other projects of GIZ/KfW and other donors.

3.1 គោលបំណងចម្បង (១​ ឬច្រើន)​ នៃបច្ចេកទេសនេះ

• កាត់បន្ថយ, បង្ការ, ស្តារឡើងវិញនូវការធ្លាក់ចុះគុណភាពដី

3.2 ប្រភេទដីប្រើប្រាស់មួយប្រភេទ (ច្រើនប្រភេទ) ដែលបានអនុវត្តបច្ចេកទេស

ដីប្រើប្រាស់ចម្រុះនៅលើដីតែមួយ:

បាទ/ចា៎

បញ្ជាក់ពីប្រភេទដីច្រើនប្រភេទ (ដីដាំដំណាំ/ដីចិញ្ចឹមសត្វ/ដីព្រៃឈើ):

• ដាំដំណាំ ចិញ្ចឹមសត្វ និងឈើ

មតិយោបល់:

major cash crop: Ground nut
major food crop: Millet
other: Sorghum, cow pea and mangoes

Major land use problems (compiler’s opinion): surface runoff, erosion by water and wind, fertility decline,

Nomadism: Yes

Semi-nomadism / pastoralism: Yes

Cut-and-carry/ zero grazing: Yes

Improved pasture: Yes

Other grazingland: agropastoralism

Selective felling of (semi-) natural forests: Yes

Forest products and services: timber, fuelwood, fruits and nuts, grazing / browsing, other forest products / uses (honey, medical, etc.)

Type of cropping system and major crops comments: farmers are mainly agropastoralists with some communities specialised on pure pastoralism

Constraints of common grazing land

Constraints of forested government-owned land or commons

Livestock density: 1-10 LU /km2

3.4 ការផ្គត់ផ្គង់ទឹក

ការផ្គត់ផ្គង់ទឹកនៅកន្លែងអនុវត្តបច្ចេកទេស:

• ទឹកភ្លៀង

មតិយោបល់:

Water supply: Also mixed rainfed - irrigated and post-flooding

3.5 ក្រុម SLM ដែលបច្ចេកទេសស្ថិតនៅក្នុង

• វិធានការអនុវត្តកាត់ទទឹងទីជម្រាល

3.6 វិធានការ SLM ដែលបញ្ចូលនូវបច្ចេកទេស

3.7 កំណត់ប្រភេទនៃការធ្លាក់ចុះគុណភាពដីសំខាន់ៗដែលបច្ចេកទេសនេះបានដោះស្រាយ

មតិយោបល់:

Secondary types of degradation addressed: Et: loss of topsoil

Main causes of degradation: soil management (Unadapted landuse methods, reduced or abandoned fallow periods), crop management (annual, perennial, tree/shrub) (Neglect of fallow periods and crop rotation), droughts (due to heat waves and unreliable rainfall), population pressure (rapidly growing population increasing pressure on land), land tenure (insecure access to land and collectively managed communal land), poverty / wealth (very poor population)

Secondary causes of degradation: deforestation / removal of natural vegetation (incl. forest fires) (deforestation through overgrazing and fire wood collection), over-exploitation of vegetation for domestic use (firewood collection), overgrazing (cattle, sheep and goats), change in temperature (Climate change: heat waves), change of seasonal rainfall (more variable onset of rain), Heavy / extreme rainfall (intensity/amounts) (more variable and intensive rains), wind storms / dust storms (frequent storms), floods (due to intensive rain storms), labour availability (some migration of men to nearby cities), education, access to knowledge and support services (high level of illiteracy)

3.8 ការពារ កាត់បន្ថយ ឬស្តារឡើងវិញនៃការធ្លាក់ចុះគុណភាពដី

បញ្ជាក់ពីគោលដៅរបស់បច្ចេកទេស ដែលផ្តោតទៅការធ្លាក់ចុះគុណភាពដី:

• ការជួសជុល/ ស្តារឡើងវិញនៃឱនភាពដីធ្ងន់ធ្ងរ

មតិយោបល់:

Secondary goals: prevention of land degradation, mitigation / reduction of land degradation

4.1 គំនូសបច្ចេកទេសនៃបច្ចេកទេសនេះ

4.2 ព័ត៌មានទូទៅដែលពាក់ព័ន្ធនឹងការគណនាធាតុចូល និងថ្លៃដើម

កំណត់រូបិយប័ណ្ណសម្រាប់ថ្លៃដើម:

• ដុល្លារ

4.3 សកម្មភាពបង្កើត

	សកម្មភាព	រយៈពេល​ (រដូវកាល)
1.	Levelling and marking out the contour lines
2.	collecting stones and loading them onto carts
3.	transporting the stones by cart
4.	constructing the bunds
5.	applying manure

4.4 ថ្លៃដើម និងធាតុចូលដែលត្រូវការសម្រាប់ការបង្កើតបច្ចេកទេស

	បញ្ជាក់ពីធាតុចូល	ឯកតា	បរិមាណ	ថ្លៃដើមក្នុងមួយឯកតា	ថ្លៃធាតុចូលសរុប	% នៃថ្លៃដើមដែលចំណាយដោយអ្នកប្រើប្រាស់ដី
កម្លាំងពលកម្ម	Levelling and construction of bunds	ha	1,0	19,32	19,32
សម្ភារៈ	Tools	ha	1,0	1,95	1,95
ផ្សេងៗ	Transport of stones	ha	1,0	15,07	15,07
ថ្លៃដើមសរុបក្នុងការបង្កើតបច្ចេកទេស					36,34
ថ្លៃដើមសរុបក្នុងការបង្កើតបច្ចេកទេសគិតជាដុល្លារ					36,34

4.5 សកម្មភាពថែទាំ

	សកម្មភាព	ពេលវេលា/ ភាពញឹកញាប់
1.	Replacing stones dislodged by animals or water flow

4.7 កត្តាសំខាន់បំផុតដែលមានឥទ្ធិពលដល់ការចំណាយ

ពណ៌នាពីកត្តាប៉ះពាល់ចម្បងៗទៅលើថ្លៃដើម:

The exact cost per hectare of constructing stone bunds depends on the distance of the site from the quarry, the size of the quarry, the inclination of the terrain, which determines the spacing between the stone bunds, and the actual amount of stones transported in each lorryload. The prices below are provided as a guide.
Supply of quarry rock/stones: 24 m3 per 400 m of bund
Labour: 30 man-days per ha
• levelling and marking out the contour lines: 1 man-day
• collecting stones and loading them onto carts:
10 man-days
• transporting the stones by cart: 10 man-days
• constructing the bunds: 9 man-days
• applying manure.
Transportation by cart:
• 20 cartloads of stones
• 20 cartloads of manure (if used).
Transportation by lorry:
• 6 lorryloads (skip loader – 4.5 m3 per load).
Other costs: equipment (pickaxes, shovels, wheelbarrows, water-tube level, etc.).

5.1 អាកាសធាតុ

5.2 សណ្ឋានដី

មតិយោបល់ និងបញ្ចាក់បន្ថែមអំពីសណ្ឋានដី :

Landforms: Also footslopes and valley floors

Altitudinal zone: 200 m a.s.l.

5.3 ដី

បើអាចសូមភ្ជាប់ការពណ៌នាពីដីឱ្យបានច្បាស់ ឬព័ត៌មានដែលអាចទទួលបាន ឧ. ប្រភេទដី, pH ដី/ ជាតិអាស៊ីត, សមត្ថភាពផ្លាស់ប្តូរកាចុង, វត្តមាននីត្រូសែន, ភាពប្រៃ ។ល។:

Soil texture (topsoil): Fine to medium (sandy to clayey loams)

5.4 ទឹកដែលអាចទាញមកប្រើប្រាស់បាន និងគុណភាពទឹក

មតិយោបល់ និងលក្ខណៈពិសេសផ្សេងៗទៀតលើគុណភាព និងបរិមាណទឹក​ :

Ground water table: > 10 m

Availability of surface water: Surface runoff generated by limited but intense rainfalls

5.5 ជីវៈចម្រុះ

5.6 លក្ខណៈនៃអ្នកប្រើប្រាស់ដីដែលអនុវត្តបច្ចេកទេស

សូមបញ្ជាក់ពីលក្ខណៈពាក់ព័ន្ធផ្សេងទៀតអំពីអ្នកប្រើប្រាស់ដី:

Population density: 10-50 persons/km2

Annual population growth: 3% - 4%

(mostly poor households below poverty line).

Off-farm income specification: men migrate temporarily or permanently to cities for off-farm income, women and men seasonally carry out paid farm work

Market orientation of production system: Most households crop for subsistence (mainly for small agropastoralists) and surplus is sold on market (medium agropastoralists). Commercial markets: some vegetable growing and pastoralists.

Level of mechanization: Ox and donkey used for animal traction

5.7 ទំហំផ្ទៃដីជាមធ្យមនៃដីប្រើប្រាស់ដោយអ្នកប្រើប្រាស់ដី ក្នុងការអនុវត្ត​បច្ចេកទេស

5.8 ភាពជាម្ចាស់ដី កម្មសិទ្ធប្រើប្រាស់ដី និងកម្មសិទ្ធប្រើប្រាស់ទឹក

ភាពជាម្ចាស់ដី:

• រដ្ឋ
• ភូមិ

កម្មសិទ្ធិប្រើប្រាស់ដី:

• ជាក្រុម (មានដែនកំណត់)
• ឯកជន

មតិយោបល់:

traditional land use rights prevail. On fields individual land use rights, communal rights on pasture and forest land (collection of wood and other products (fruits, medicinal plants))

Land ownership: Also individual not titled

5.9 ការប្រើប្រាស់សេវាកម្ម និងហេដ្ឋារចនាសម្ព័ន្ធ

6.1 ផលប៉ះពាល់ក្នុងបរិវេណអនុវត្តបច្ចេកទេសដែលកើតមាន

ផលប៉ះពាល់លើសេដ្ឋកិច្ចសង្គម

ផលិតផល

ទឹកដែលអាចទាញមកប្រើប្រាស់បាន និងគុណភាពទឹក

ចំណូល និងថ្លៃដើម

ផលប៉ះពាល់ទៅលើវប្បធម៌សង្គម

ផលប៉ះពាល់ទៅលើអេកូឡូស៊ី

វដ្តទឹក/លំហូរ

ដី

ជីវចម្រុះ៖ ដំណាំ, សត្វ

ការកាត់បន្ថយហានិភ័យនៃគ្រោះមហន្តរាយ និងគ្រោះអាកាសធាតុ

ផលប៉ះពាល់ទៅលើអេកូឡូស៊ីផ្សេងៗ

6.2 ផលប៉ះពាល់ក្រៅបរិវេណអនុវត្តបច្ចេកទេសដែលកើតមាន

6.3 ភាពប្រឈម និងភាពរួសនៃបច្ចេកទេសទៅនឹងការប្រែប្រួលអាកាសធាតុ និងគ្រោះអាកាសធាតុ/ គ្រោះមហន្តរាយ (ដែលដឹងដោយអ្នកប្រើប្រាស់ដី)

ការប្រែប្រួលអាកាសធាតុ

ការប្រែប្រួលអាកាសធាតុ

	រដូវកាល	កើនឡើង ឬថយចុះ	លក្ខណៈឆ្លើយតបនៃបច្ចេកទេសទៅនឹងការប្រែប្រួលអាកាសធាតុ
សីតុណ្ហភាពប្រចាំឆ្នាំ		កើនឡើង	ល្អ

គ្រោះអាកាសធាតុ (មហន្តរាយ) ​

គ្រោះមហន្តរាយធម្មជាតិ

	លក្ខណៈឆ្លើយតបនៃបច្ចេកទេសទៅនឹងការប្រែប្រួលអាកាសធាតុ
ព្យុះភ្លៀងតាមតំបន់	មិនល្អ
ព្យុះកំបុតត្បូងតាមតំបន់	ល្អ

គ្រោះមហន្តរាយអាកាសធាតុ

	លក្ខណៈឆ្លើយតបនៃបច្ចេកទេសទៅនឹងការប្រែប្រួលអាកាសធាតុ
រាំងស្ងួត	ល្អ

គ្រោះមហន្តរាយទឹក

	លក្ខណៈឆ្លើយតបនៃបច្ចេកទេសទៅនឹងការប្រែប្រួលអាកាសធាតុ
ទឹកជំនន់ទូទៅ (ទន្លេ)	មិនល្អ

ផលវិបាកដែលទាក់ទងនឹងបរិយាកាសផ្សេងៗទៀត

ផលវិបាកដែលទាក់ទងនឹងបរិយាកាសផ្សេងៗទៀត

	លក្ខណៈឆ្លើយតបនៃបច្ចេកទេសទៅនឹងការប្រែប្រួលអាកាសធាតុ
កាត់បន្ថយពេលដាំដុះ	មិនស្គាល់

6.4 ការវិភាគថ្លៃដើម និងអត្ថប្រយោជន៍

តើផលចំណេញ និងថ្លៃដើមត្រូវបានប្រៀបធៀបគ្នាយ៉ាងដូចម្តេច (ទស្សនៈរបស់អ្នកប្រើប្រាស់ដី)?

តើផលចំណេញ និងការថែទាំ/ ជួសជុលត្រូវបានប្រៀបធៀបគ្នាយ៉ាងដូចម្តេច (ទស្សនៈរបស់អ្នកប្រើប្រាស់ដី)?

6.5 ការទទួលយកបច្ចេកទេស

ក្នុងចំណោមគ្រួសារទាំងអស់ដែលបានអនុវត្តបច្ចេកទេស តើមានប៉ុន្មាន​គ្រួសារ​ដែល​ចង់​ធ្វើ​ដោយ​ខ្លួន​ឯង ដោយមិន​ទទួល​បាន​សម្ភារៈ​លើក​​ទឹកចិត្ត/​ប្រាក់ឧបត្ថម្ភ?​:

• 51-90%

មតិយោបល់:

Comments on acceptance with external material support: While in emergency programs erosion control structures are mostly implemented through cash/food for work this is not the case in natural resource programs. As concerns German Development Cooperation, cash/food for work has been used during the 80ies and 90ies to implement stone bunds. Thereafter most programs switched to a voluntary approach where only Tools and transport were provided but all labour has been provided by the beneficiaries without payment.

80% of land user families have adopted the Technology without any external material support

There is a little trend towards spontaneous adoption of the Technology

Comments on adoption trend: The success of this measure and implementation on a wide scale depend to a large extent on whether grants are available to cover the cost of transporting the stones required to the site, good community organisation and the capacity of the community to mobilise the necessary labour, the contribution required from the farmers.
The farmers’ commitment to implementing the measure largely depends on whether they are allowed to choose the sites to be improved in their area. Forcing them to begin the improvement work upstream, as dictated by the traditional watershed development approach, has often proved counterproductive. Most communities prefer to improve individual plots first in order to achieve immediate effects on crop production and leave the treatment of forest/ rangeland areas as a second step.

6.7 ភាពខ្លាំង/ គុណសម្បត្តិ/ ឱកាសនៃបច្ចេកទេស

ភាពខ្លាំង/ គុណសម្បត្តិ/ ឱកាស​ ទស្សនៈរបស់បុគ្គលសំខាន់ៗ
There is evidence that bunds that have been in place for over 15 years have positive effects on yields. Grain yields increase by more than 40% for millet up to 15 years after the bunds were established, and there is no evidence to suggest that yields decline with time. This can be explained by improved soil structure, which increases infiltration, even after the bunds are completely silted up.
The lifespan of a stone bund is over 20 years. There is a progressive build-up of sediment behind the bunds, resulting in the formation of terraces. Although the capacity of the bunds to retain water declines as the sediment builds up, soil infiltration capacity increases, thanks to improved soil structure, and the slope becomes gentler thanks to the terracing effect. How can they be sustained / enhanced? Farmers can maintain water retention capacity by raising the height of the existing bunds. In some places, farmers take the stones from the original bunds when a ridge of vegetation has been established and use them to form new bunds between the old ones.
The decrease in surface runoff in the treated area reduces the flow of floodwater and the amount of sediment carried by the water downstream, thereby protecting the fertile land in the valley bottoms from siltation and gully erosion. How can they be sustained / enhanced? In order to optimise the positive effects of stone bunds, it is important to ensure that they are constructed closely following the natural contour of the land and in accordance with the established technical standards.
In dry years, while unimproved land produces nothing, land protected by stone bunds can still produce a harvest. How can they be sustained / enhanced? When stone bunds are used in combination with zai planting pits, sorghum yields can increase by 114-124%. When used in conjunction with the application of the right amount of organic fertiliser, sorghum yields can be doubled.
Higher crop production improves household food security in proportion to the area of a farm improved with bunds. Under the PASP in Niger, an average of 16% of the area of a farm was improved with stone bunds, resulting in an increase of between 8% and 33% in annual output with no other additional measures.

6.8 ភាពខ្សោយ/ គុណវិបត្តិ/ ហានិភ័យនៃបច្ចេកទេស និងវិធីសាស្ត្រដោះស្រាយ

ភាពខ្សោយ/ គុណវិបត្តិ/ ហានិភ័យ ទស្សនៈរបស់អ្នកចងក្រងឬបុគ្គលសំខាន់ៗ	តើបច្ចេកទេសទាំងនោះបានដោះស្រាយបញ្ហាដូចម្តេច?
In wet years, the bunds may cause waterlogging in some parts of the field, which can adversely affect some crops.	If this happens, farmers must open up a gap in the bunds to drain off the water.

7.1 វិធីសាស្ត្រ/ ប្រភពនៃព័ត៌មាន

7.3 ការភ្ជាប់ទៅកាន់ព័ត៌មានពាក់ព័ន្ធលើប្រព័ន្ធអនឡាញ

ចំណងជើង/ ពណ៌នា:

Good Practices in Soil and Water Conservation. A contribution to adaptation and farmers resilience towards climate change in the Sahel. Published by GIZ in 2012.

វេបសាយ:

http://agriwaterpedia.info/wiki/Main_Page