Area closure on degraded lands [埃塞俄比亚]
- 创建:
- 更新:
- 编制者: Gizaw Desta Gessesse
- 编辑者: –
- 审查者: Deborah Niggli
Yetrakot Meret mekelel (Amharic)
technologies_1598 - 埃塞俄比亚
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全部展开 全部收起1. 一般信息
1.2 参与该技术评估和文件编制的资源人员和机构的联系方式
SLM专业人员:
Bekure Melese
WLRC
埃塞俄比亚
有助于对技术进行记录/评估的项目名称(如相关)
Water and Land Resource Centre Project (WLRC)1.3 关于使用通过WOCAT记录的数据的条件
编制者和关键资源人员接受有关使用通过WOCAT记录数据的条件。:
是
1.4 所述技术的可持续性声明
这里所描述的技术在土地退化方面是否存在问题,导致无法被认为是一种可持续的土地管理技术?:
否
1.5 请参阅有关SLM方法的问卷
'Cut and Carry' Grazing system or 'Zero Grazing' … [埃塞俄比亚]
Cut and carry grazing system (alternatively called zero grazing) is an approach where the community is consulted to identify and agree on areas to be closed and protected from free grazing; establish user groups are established to share the fodder biomass harvested from communal closed areas equitably; they utilize tree/shrub …
- 编制者: Gizaw Desta Gessesse
2. SLM技术的说明
2.1 技术简介
技术定义:
Area closure on degraded lands is a land management practice used to rehabilitate and conserve the natural resource bases, and enhance its natural regeneration and restoring capacity and productive functions by excluding animal and human interferences through community consultation and collective actions.
2.2 技术的详细说明
说明:
Area closure is a land management practice that helps to rehabilitate degraded lands, restore the biophysical conditions like soil, vegetation and hydrology by avoiding the interference of animals and human. Because of over grazing and erosion impact, areas delineated for closure are usually degraded shrub or pasture lands that served for grazing. First of all, implementing area closure requires continuous dialogue and discussion with community to reach consensus to close. The community wants to make sure they have benefited from the technology as the land was serving for grazing. They should take the responsibility and create sense of ownership to implement conservation measures, protect and maintain closure areas, and regulate utilization of benefits gained out of it. Questions raised from the community must be discussed thoroughly ahead of the implementation. What part of the degraded land? For what purpose the area is closed? Who are the users? Who are responsible to protect and manage the developed resourcess? How is the benefit sharing among identified users? Commonly, the shared benefits from area closures are hay for livestock through cut-and-carry system, timbers from plantations, and honey production.
Depending on the soil, rainfall and slope conditions different structural and vegetative measures are integrated to enhance the fast regeneration of plant species, restore the soil and increase water availability. It includes enrichment used to rehabilitate and increase the vegetation cover, vegetative and structural measures to retain the soil and water on its place. Structures such as hillside terrace often integrated with grass or shrub hedgerows is used to control soil erosion. In-situ water harvesting structures such as trenches or half moon or eye brow are used to harvest and infiltrate rain or runoff water to increase regeneration and survival of planted trees. Trees and/or shrub species that have high rehabilitation and multipurpose values are used as enrichment plantations. Closed areas need collective action to protect, maintain and manage the common resources. Collective user rights have to be entitled to bring equity on resource sharing and minimize social conflicts.
The purposes of area closure are: 1) rehabilitate degraded lands, 2) protect and restore the natural resource base, and 3) change into productive land and enhance economic and environmental functions of rehabilitated lands.
Implementation of area closure begins with the selection and demarcation of area through genuine participation of land users. After identifying the area to be closed, at establishment stage construction of ditches and terraces is made using stones combined with grasses or shrubs of multipurpose value such as Vetiver grass, Dinsho grass, Bana grass, susbania, etc. Depending on site conditions, enrichment tree species which have rehabilitation and soil restoration purposes are planted in the form of wood lot or scattered tree plantation. Among the common species, A. albida, A. saligna, A. decurrense, Gravilia robusta, etc. are used to rehabilitate and serve as fuel wood and timber. In moisture stress areas structures like trench, level bunds, and half moon should be constructed to increase survival rate of planted tree/shrub species whereas in areas having sufficient moisture these structures, depending on the landforms and soil drainage conditions, help to increase infiltration and recharging of ground water in downstream areas. Therefore, site selection and demarcation, construction of soil conservation and moisture conservation structures, and seedling management and plantation of multipurpose trees, shrubs and grasses are the activities accomplished at establishment stage of area closure. The required inputs are stones, seeds/seedlings, grass cuttings/splits, hand tools, and collective labor. For recurrent maintenance activities, seedlings and cuttings for re-plantation purpose or replace dead seedlings, stones to repair damage stone terraces and moisture conservation structures. Harvesting and transporting of area closure products such as grass and timber become a recurrent activity. Person days per hectare per year required for plantation (preparation of holes and planting) is 11.5, for harvesting and transporting harvested grass is 30, and for terrace construction is 26.5.
Area closure management is commonly practiced on degraded hills where soil is highly depleted, its water holding capacity is low, and vegetation is denuded. Usually degraded lands are used to serve for communal grazing system. The degree of land degradation becomes severe where there are high livestock and human population pressure. Management of closure area and the benefit sharing has to be regulated using agreed bylaws.
The living condition depends on subsistence crop-livestock mixed farming. On average households have 5-6 family size. Crop production is meant for home consumption with small surplus for local market. The services related to water supply, energy supply, and infrastructure are low. Besides it is an asset, animals often used to cope shocks during drought periods.
2.3 技术照片
2.5 已应用该技术的、本评估所涵盖的国家/地区/地点
国家:
埃塞俄比亚
区域/州/省:
Amhara National Regional State
有关地点的进一步说明:
Mecha / Yilmana Densa / Bahir Dar Zuria
2.6 实施日期
如果不知道确切的年份,请说明大概的日期:
- 不到10年前(最近)
2.7 技术介绍
详细说明该技术是如何引入的:
- 通过项目/外部干预
注释(项目类型等):
Area closure as an integrated SLM technology is practiced in recent years. However, the land users have their own traditional practice by closing grass lands or shrub lands during the rainy season.
3. SLM技术的分类
3.1 该技术的主要目的
- 保护生态系统
3.2 应用该技术的当前土地利用类型
牧场
粗放式放牧场:
- 半游牧/游牧
集约放牧/饲料生产:
- 收割和携带/零放牧
混合(作物/放牧/树木),包括农林
- 农牧业
注释:
Major land use problems (compiler’s opinion): Land degradation due to different forms of soil erosion and nutrient depletion, excess removal of crop residues, excessive overgrazing, shortage of pasture lands and its low productivity, excessive and inappropriate construction of traditional ditches, and increased demand of trees for the purpose of fuel wood and timber.
Major land use problems (land users’ perception): Soil erosion and soil nutrient depletion, shortage of cultivated land, shortage of grazing land and wood for fuel wood
3.3 有关土地利用的更多信息
该技术所应用土地的供水:
- 雨养
每年的生长季节数:
- 1
具体说明:
Longest growing period in days: 220, Longest growing period from month to month: May to December; Second longest growing period in days: 180, Second longest growing period from month to month: June to November
牲畜密度(如相关):
> 100 LU /km2
3.4 该技术所属的SLM组
- 区域封闭(停止使用,支持恢复)
3.5 技术传播
具体说明该技术的分布:
- 均匀地分布在一个区域
如果该技术均匀地分布在一个区域上,请注明覆盖的大致区域。:
- 1-10 平方千米
3.6 包含该技术的可持续土地管理措施
植物措施
- V1:乔木和灌木覆盖层
- V2:草和多年生草本植物
结构措施
- S2:堤、岸
- S3:分级沟渠、渠道、水道
- S4:平沟、坑
管理措施
- M1:改变土地使用类型
- M2:改变管理/强度级别
注释:
Type of vegetative measures: aligned: -contour, scattered / dispersed, in blocks
3.7 该技术强调的主要土地退化类型
土壤水蚀
- Wt:表土流失/地表侵蚀
- Wo:场外劣化效应
化学性土壤退化
- Cn:肥力下降和有机质含量下降(非侵蚀所致)
生物性退化
- Bc:植被覆盖的减少
- Bh:栖息地丧失
注释:
Main causes of degradation: deforestation / removal of natural vegetation (incl. forest fires), overgrazing, population pressure, governance / institutional
Secondary causes of degradation: soil management, over-exploitation of vegetation for domestic use, Heavy / extreme rainfall (intensity/amounts), land tenure, education, access to knowledge and support services
3.8 防止、减少或恢复土地退化
具体数量名该技术与土地退化有关的目标:
- 减少土地退化
- 修复/恢复严重退化的土地
4. 技术规范、实施活动、投入和成本
4.1 该技术的技术图纸
4.2 技术规范/技术图纸说明
Integrated practices of area closure including hillside bunds, trenches, micro-basins, and trees/shrubs
Location: Debre Yacob Learning Watershed. Mecha/West Gojam/Amhara
Date: 2014-5-23
Technical knowledge required for field staff / advisors: moderate (Field staffs need to acquire technical knowledge on how to integrate different practices and strategies depending on the conditions and degree of degradation.)
Technical knowledge required for land users: low (Land users require low knowledge. Once they implement practices in the closure area, they are able to coordinate and respect the bylaws and equitable distribution of benefits.)
Main technical functions: control of raindrop splash, control of dispersed runoff: retain / trap, control of concentrated runoff: impede / retard, improvement of ground cover, increase of biomass (quantity)
Secondary technical functions: control of concentrated runoff: drain / divert, improvement of topsoil structure (compaction), increase in organic matter, increase / maintain water stored in soil
Aligned: -contour
Vegetative material: T : trees / shrubs, G : grass
Number of plants per (ha): 4000-6000
Spacing between rows / strips / blocks (m): 5
Vertical interval within rows / strips / blocks (m): 0.5-1.0
Width within rows / strips / blocks (m): 0.5
Scattered / dispersed
Vegetative material: T : trees / shrubs
Number of plants per (ha): 160
In blocks
Vegetative material: T : trees / shrubs
Spacing between rows / strips / blocks (m): 2
Vertical interval within rows / strips / blocks (m): 2
Trees/ shrubs species: Gravilia, Susbania, Acacia decurrence
Grass species: Napier
Slope (which determines the spacing indicated above): 20-30%
Gradient along the rows / strips: 0.5%
Diversion ditch/ drainage
Depth of ditches/pits/dams (m): 0.3-0.7
Width of ditches/pits/dams (m): 1.2-2.8
Length of ditches/pits/dams (m): 100-250
Waterway
Depth of ditches/pits/dams (m): 0.3
Width of ditches/pits/dams (m): 1.5-2.0
Bund/ bank: level
Spacing between structures (m): 5
Height of bunds/banks/others (m): 0.5
Width of bunds/banks/others (m): 1-1.5
Slope (which determines the spacing indicated above): 15-35%
Vegetation is used for stabilisation of structures.
Change of land use type: Initially, the land is highly degraded and waste land. After an increase in vegetation cover and biomass, its use is thus changed from waste/shrub land/open grazing to cut-and-carry grazing system
Change of land use practices / intensity level: The land use management is changed from open access /communal grazing or shrub land to regulated or organized form of land use management
4.3 有关投入和成本计算的一般信息
其它/国家货币(具体说明):
ETB
注明美元与当地货币的汇率(如相关):1美元=:
20.0
注明雇用劳工的每日平均工资成本:
2.50
4.4 技术建立活动
活动 | 措施类型 | 时间 | |
---|---|---|---|
1. | Preparation of seedlings | 植物性的 | March-May |
2. | Transporting seedlings | 植物性的 | July |
3. | Transporting grass splits | 植物性的 | July |
4. | Sowing seeds on bunds | 植物性的 | July |
5. | Planting of trees and shrubs | 植物性的 | July |
6. | Planting of grass splits or cuttings | 植物性的 | July |
7. | Construction of bunds or terraces | 结构性的 | February-April |
8. | Construction of cutoff drains and ditches | 结构性的 | Fegruary-April |
9. | Construction of waterways | 结构性的 | February-April |
10. | Surveying or layout of structures | 结构性的 | January-March |
11. | Consultation of the community | 管理 | |
12. | Establish bylaws to control free grazing | 管理 | |
13. | Establish user groups and arrange equitable benefit sharing | 管理 |
4.5 技术建立所需要的费用和投入
对投入进行具体说明 | 单位 | 数量 | 单位成本 | 每项投入的总成本 | 土地使用者承担的成本% | |
---|---|---|---|---|---|---|
劳动力 | labour | ha | 1.0 | 1766.0 | 1766.0 | 80.0 |
设备 | tools | ha | 1.0 | 300.6 | 300.6 | 50.0 |
植物材料 | seedlings | ha | 1.0 | 405.6 | 405.6 | 100.0 |
植物材料 | seeds | ha | 1.0 | 20.0 | 20.0 | 100.0 |
施工材料 | stone | ha | 1.0 | 1300.0 | 1300.0 | 100.0 |
技术建立所需总成本 | 3792.2 |
注释:
Duration of establishment phase: 15 month(s)
4.6 维护/经常性活动
活动 | 措施类型 | 时间/频率 | |
---|---|---|---|
1. | Preparation of seedlings | 植物性的 | March-May |
2. | Seedling transportation | 植物性的 | July |
3. | Grass split transportation | 植物性的 | July |
4. | Planting seedlings | 植物性的 | July |
5. | Planting grass splits | 植物性的 | July |
6. | Maintenance of bunds / cutoff drains | 结构性的 | |
7. | Enforcing bylaws | 管理 | Throught the year |
8. | Benefit sharing among user groups | 管理 | Throughout the year |
4.7 维护/经常性活动所需要的费用和投入(每年)
对投入进行具体说明 | 单位 | 数量 | 单位成本 | 每项投入的总成本 | 土地使用者承担的成本% | |
---|---|---|---|---|---|---|
劳动力 | labour | ha | 1.0 | 624.0 | 624.0 | 29.0 |
植物材料 | seedlings | ha | 1.0 | 250.0 | 250.0 | 100.0 |
技术维护所需总成本 | 874.0 |
注释:
Machinery/ tools: Spade, pickaxe, crowbar,
4.8 影响成本的最重要因素
描述影响成本的最决定性因素:
The costs of area closure affected by the labour availability, regeneration capacity of trees on the degraded lands
5. 自然和人文环境
5.1 气候
年降雨量
- < 250毫米
- 251-500毫米
- 501-750毫米
- 751-1,000毫米
- 1,001-1,500毫米
- 1,501-2,000毫米
- 2,001-3,000毫米
- 3,001-4,000毫米
- > 4,000毫米
农业气候带
- 半湿润
Thermal climate class: subtropics
5.2 地形
平均坡度:
- 水平(0-2%)
- 缓降(3-5%)
- 平缓(6-10%)
- 滚坡(11-15%)
- 崎岖(16-30%)
- 陡峭(31-60%)
- 非常陡峭(>60%)
地形:
- 高原/平原
- 山脊
- 山坡
- 山地斜坡
- 麓坡
- 谷底
垂直分布带:
- 0-100 m a.s.l.
- 101-500 m a.s.l.
- 501-1,000 m a.s.l.
- 1,001-1,500 m a.s.l.
- 1,501-2,000 m a.s.l.
- 2,001-2,500 m a.s.l.
- 2,501-3,000 m a.s.l.
- 3,001-4,000 m a.s.l.
- > 4,000 m a.s.l.
5.3 土壤
平均土层深度:
- 非常浅(0-20厘米)
- 浅(21-50厘米)
- 中等深度(51-80厘米)
- 深(81-120厘米)
- 非常深(> 120厘米)
土壤质地(表土):
- 中粒(壤土、粉土)
- 细粒/重质(粘土)
表土有机质:
- 低(<1%)
5.4 水资源可用性和质量
地下水位表:
> 50米
地表水的可用性:
中等
水质(未处理):
不良饮用水(需要处理)
5.5 生物多样性
物种多样性:
- 低
5.6 应用该技术的土地使用者的特征
生产系统的市场定位:
- 生计(自给)
非农收入:
- 低于全部收入的10%
相对财富水平:
- 贫瘠
- 平均水平
个人或集体:
- 团体/社区
性别:
- 女人
- 男人
说明土地使用者的其他有关特征:
Land users applying the Technology are mainly common / average land users
Difference in the involvement of women and men: Women has their own role in the establishment of the rea closure by collecting stones, support construction and planting activities. In addition they will harvest and transport fodder for livestock
Population density: 200-500 persons/km2
Annual population growth: 2% - 3%
80% of the land users are average wealthy.
20% of the land users are poor.
5.7 应用该技术的土地使用者拥有或租用的平均土地面积
- < 0.5 公顷
- 0.5-1 公顷
- 1-2 公顷
- 2-5公顷
- 5-15公顷
- 15-50公顷
- 50-100公顷
- 100-500公顷
- 500-1,000公顷
- 1,000-10,000公顷
- > 10,000公顷
这被认为是小规模、中规模还是大规模的(参照当地实际情况)?:
- 小规模的
5.8 土地所有权、土地使用权和水使用权
土地所有权:
- 州
用水权:
- 自由进入(无组织)
- 社区(有组织)
5.9 进入服务和基础设施的通道
健康:
- 贫瘠
- 适度的
- 好
教育:
- 贫瘠
- 适度的
- 好
技术援助:
- 贫瘠
- 适度的
- 好
就业(例如非农):
- 贫瘠
- 适度的
- 好
市场:
- 贫瘠
- 适度的
- 好
能源:
- 贫瘠
- 适度的
- 好
道路和交通:
- 贫瘠
- 适度的
- 好
饮用水和卫生设施:
- 贫瘠
- 适度的
- 好
金融服务:
- 贫瘠
- 适度的
- 好
6. 影响和结论性说明
6.1 该技术的现场影响
社会经济效应
生产
饲料生产
注释/具体说明:
Mainly serve for grass harvest
畜牧生产
注释/具体说明:
Cut and carry improve the production
生产区域
注释/具体说明:
By improving the land use management, production area for pasture increased
收入和成本
收入来源的多样性
注释/具体说明:
People try to diverse apiculture production in closed areas
工作量
注释/具体说明:
Labor requirement to harvest and transport fodder and pasture increase
社会文化影响
社区机构
注释/具体说明:
Establishment of user groups and watershed users association
SLM/土地退化知识
注释/具体说明:
Increase the level of awareness that area closure can shortly reverse land degradation
冲突缓解
注释/具体说明:
Reduce conflict arise due to pasture shortage
社会经济弱势群体的情况
注释/具体说明:
Some rural unemployed youths get employed in apiculture production and fruit production
contribution to human well-being
注释/具体说明:
The livestock production is moderately improved due to increase in biomass/ pasture harvest
生态影响
水循环/径流
水量
地表径流
地下水位/含水层
土壤
土壤水分
土壤覆盖层
土壤流失
生物多样性:植被、动物
生物量/地上C
植物多样性
栖息地多样性
减少气候和灾害风险
火灾风险
6.2 该技术的场外影响已经显现
旱季稳定可靠的水流
SLM之前的数量:
End of Nov
SLM之后的数量:
Mar-April
注释/具体说明:
Because of high vegetation cover, the recharrging capacity improved resulting in prolonging the stream flow/baseflow
下游洪水
下游淤积
6.3 技术对渐变气候以及与气候相关的极端情况/灾害的暴露和敏感性(土地使用者认为的极端情况/灾害)
气候有关的极端情况(灾害)
气象灾害
该技术是如何应对的? | |
---|---|
局地暴雨 | 好 |
气候灾害
该技术是如何应对的? | |
---|---|
干旱 | 好 |
水文灾害
该技术是如何应对的? | |
---|---|
比较和缓的(河道)洪水 | 不好 |
6.4 成本效益分析
技术收益与技术建立成本相比如何(从土地使用者的角度看)?
短期回报:
稍微积极
长期回报:
积极
技术收益与技术维护成本/经常性成本相比如何(从土地使用者的角度看)?
短期回报:
积极
长期回报:
非常积极
注释:
Short term economic benefits can be attained by harvesting forage biomass for livestock while in the long term downstream agricultural productivity can be improved as they witnessed the change in stream flows to be used for irrigation. This is very much pronounced in Aba Gerima watershed where farmers in the downstream get to access more water.
6.5 技术采用
注释:
The technology is implemented in group or at community level.
The spontaneous adoption of this technology is possible without integrating plantations of improved trees/shrubs and grasses
There is a moderate trend towards spontaneous adoption of the Technology
Adoption to area closure is increasing as it provides better pasture for livestock and benefit those who do not have power or for poor community groups
6.7 该技术的优点/长处/机会
土地使用者眼中的长处/优势/机会 |
---|
Increase in vegetation cover and biomass production for livestock feed |
Increase the duration and flow of streams |
Decrease erosion |
Decrease transmission of animal disease often a problem during open grazing system |
编制者或其他关键资源人员认为的长处/优势/机会 |
---|
Increase the fodder and grass biomass production for livestock feed |
Increase the regeneration of lost plant diversities |
Create alternative livelihood options (off farm activities like honey production, timber, tree or fodder seed production) |
Enhance the micro-climatic conditions and on-site vegetation cover, organic matter, and soil water holding capacity. In addition it improves off-site surface and subsurface water flows |
6.8 技术的弱点/缺点/风险及其克服方法
土地使用者认为的弱点/缺点/风险 | 如何克服它们? |
---|---|
Land users' perceived that implementation of the technology decreases open access to communal pasture lands to maximize their benefit | Awareness creation activities has to be provided |
Shortage of labor to harvest and transport forages to feed animals | Cost effective technologies to prepare feed, handle and transport forage has to be introduced and adopted. It can be overcomed by organizing service provider groups. |
The amount of pasture/fodder produced and shared among users is much less than the feed requirement of all animals hold by a household | Introduce fodder species producing high biomass and high quality fodder; decrease livestock number per household. |
编制者或其他关键资源人员认为的弱点/缺点/风险 | 如何克服它们? |
---|---|
Labor constraint for cut-and -carry for stall feeding | It can be sustained through organizing service providers groups |
Stall feeding restricted the cross breeding of animals in the village easily accessible during open grazing | Artificial insemination and bull services and synchronization breeding system has to be promoted |
7. 参考和链接
7.1 信息的方法/来源
- 实地考察、实地调查
- 与土地使用者的访谈
7.2 参考可用出版物
标题、作者、年份、ISBN:
Sustaining the win-win benefits of improved grazing land management in EthiopiaPost written by Wolde Mekuria, WLE. March 30, 2015
可以从哪里获得?成本如何?
WLE post
标题、作者、年份、ISBN:
http://www.bioone.org/doi/pdf/10.1659/0276-4741(2005)025%5B0044%3ATROCIC%5D2.0.CO%3B2
标题、作者、年份、ISBN:
Vegetation Improvement in Communal Closed Areas in Tigray, Ethiopia.Sarah Tewolde-Berhan 1,4, Ralph Mitlöhner 2, Bart Muys3 , and Mitiku Haile 4
标题、作者、年份、ISBN:
Natural Regeneration Practice in Degraded High Lands of Ethiopia Through Area Enclosure Wondie Mebrat, Department of Biology, Adigrat University, Adigrat, Tigray, Ethiopia, 2015
标题、作者、年份、ISBN:
Area Closure: Rehabilitation of Degraded Lands and Grasslands and its Multiple Benefits. WLRC Brief No. 2. June 2015
可以从哪里获得?成本如何?
www.wlrc-eth.org
链接和模块
全部展开 全部收起链接
'Cut and Carry' Grazing system or 'Zero Grazing' … [埃塞俄比亚]
Cut and carry grazing system (alternatively called zero grazing) is an approach where the community is consulted to identify and agree on areas to be closed and protected from free grazing; establish user groups are established to share the fodder biomass harvested from communal closed areas equitably; they utilize tree/shrub …
- 编制者: Gizaw Desta Gessesse
模块
无模块