Difference between revisions of "Mitigation and Intervention Techniques Related to Micro-hydro Power (MHP) Projects"
From energypedia
***** (***** | *****) m |
***** (***** | *****) m |
||
| Line 1: | Line 1: | ||
= Overview<br/> = | = Overview<br/> = | ||
| − | The identification of appropriate mitigation and intervention techniques on the basis of the [[ | + | |
| + | The identification of appropriate mitigation and intervention techniques on the basis of the [[Environment_Assessment_Related_to_Micro-hydro_Power_(MHP)_Projects_in_Ethiopia|Environment Assessment]] is crucial for the implementation of a successful [[Watershed_Action_Planning_related_to_Micro-hydro_Power_(MHP)_Projects_in_Ethiopia|Watershed Action Plan]] in order to achieve a sustainable use of the catchment area and thus the MHP project. | ||
<br/> | <br/> | ||
| Line 9: | Line 10: | ||
<br/> | <br/> | ||
| + | <br/> | ||
= Biophysical Measures<br/> = | = Biophysical Measures<br/> = | ||
== Gully Control<br/> == | == Gully Control<br/> == | ||
| − | ► [[Micro- | + | |
| + | ► [[Micro-hydro_Power_(MHP)_Projects_-_Mitigation_and_Intervention_Techniques_-_Gully_Control|Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Gully Control]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
== Agro-forestry, Forage Development and Forestry<br/> == | == Agro-forestry, Forage Development and Forestry<br/> == | ||
| − | ► [[Micro- | + | |
| + | ► [[Micro-hydro_Power_(MHP)_Projects_-_Mitigation_and_Intervention_Techniques_-_Agro-forestry,_Forage_Development_and_Forestry|Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Agro-forestry, Forage Development and Forestry]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
== Soil Fertility Management and Biological Soil Conservation<br/> == | == Soil Fertility Management and Biological Soil Conservation<br/> == | ||
| − | ► [[Micro- | + | |
| + | ► [[Micro-hydro_Power_(MHP)_Projects_-_Mitigation_and_Intervention_Techniques_-_Soil_Fertility_Management_and_Biological_Soil_Conservation|Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Soil Fertility Management and Biological Soil Conservation]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
== Flood Control and Improved Drainage<br/> == | == Flood Control and Improved Drainage<br/> == | ||
| − | ► [[Micro- | + | |
| + | ► [[Micro-hydro_Power_(MHP)_Projects_-_Mitigation_and_Intervention_Techniques_-_Flood_Control_and_Improved_Drainage|Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Flood Control and Improved Drainage]]<br/> | ||
<br/> | <br/> | ||
| + | <br/> | ||
== Physical Soil and Water Conservation<br/> == | == Physical Soil and Water Conservation<br/> == | ||
| − | ► [[Micro- | + | |
| + | ► [[Micro-hydro_Power_(MHP)_Projects_-_Mitigation_and_Intervention_Techniques_-_Physical_Soil_and_Water_Conservation|Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Physical Soil and Water Conservation]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
== Water Harvesting == | == Water Harvesting == | ||
| − | ► [[Micro- | + | |
| + | ► [[Micro-hydro_Power_(MHP)_Projects_-_Mitigation_and_Intervention_Techniques_-_Water_Harvesting|Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Water Harvesting]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
= Education and Training<br/> = | = Education and Training<br/> = | ||
| − | ► [[ | + | |
| + | ► [[Watershed_Action_Planning_related_to_Micro-hydro_Power_(MHP)_Projects_in_Ethiopia#Training|Watershed Action Planning related to Micro-hydro Power (MHP) Projects in Ethiopia - Training]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
= Participatory Approach = | = Participatory Approach = | ||
| − | ► [[ | + | |
| + | ► [[Watershed_Planning_Team_related_to_Micro-hydro_Power_(MHP)_Projects_in_Ethiopia#Participatory_Approach|Watershed Planning Team related to Micro-hydro Power (MHP) Projects in Ethiopia - Participatory Approach]] | ||
<br/> | <br/> | ||
| + | <br/> | ||
= Improving the Environmental Condition of the Catchment = | = Improving the Environmental Condition of the Catchment = | ||
| + | |||
Adetailed list of mitigation and intervention techniques and the respective application can be found in | Adetailed list of mitigation and intervention techniques and the respective application can be found in | ||
| Line 71: | Line 90: | ||
<br/> | <br/> | ||
| + | <br/> | ||
=== Fenced vs. Unfenced Springs / Wetlands<br/> === | === Fenced vs. Unfenced Springs / Wetlands<br/> === | ||
| − | Springs and wetlands not only guarantee the discharge in dry season, also they have a great retention capacity during and after rains. Springs are sensitive areas that react to disturbances easily. Protection of springs and wetlands is thus crucial for the sustainable use of the MHP projects. Protection measurements might include fencing (to protect the areas from [[ | + | |
| + | Springs and wetlands not only guarantee the discharge in dry season, also they have a great retention capacity during and after rains. Springs are sensitive areas that react to disturbances easily. Protection of springs and wetlands is thus crucial for the sustainable use of the MHP projects. Protection measurements might include fencing (to protect the areas from [[Causes_and_Features_of_Watershed_Degradation_related_to_MHP_Projects#Changes_in_Soil_Texture_and_Cattle_Step|cattle step]] and thus soil compaction), protection of [[Causes_and_Features_of_Watershed_Degradation_related_to_MHP_Projects#Deforestation_and_Destruction_of_Natural_Vegetation|natural vegetation]] around the springs, protection of a natural humus layer (in order to sustain sufficient infiltration and thus groundwater recharge). Furthermore fencing can help to improve the water quality, since pollution due to agricultural and pastoral use can be prevented<ref>HELVETAS (2005): Helvetas Wasser Fact Sheet: Quellen und Quellschutz.</ref>. | ||
<br/> | <br/> | ||
| Line 79: | Line 100: | ||
<br/> | <br/> | ||
| + | <br/> | ||
=== Buffered vs. Unbuffered Riverbanks / Wetlands<br/> === | === Buffered vs. Unbuffered Riverbanks / Wetlands<br/> === | ||
| + | |||
A buffer typically consists of a band of vegetation along a wetland or water body, preferably natural habitat, but including previously altered, stable native or introduced species. A buffer can perform a variety of functions, which can improve the environmental condition of a watershed, such as sediment removal and erosion control, runoff reduction through infiltration, reduction of human impacts by limiting easy access as well as barrier to invasion of exotic species<ref>GALE, J.A. (unknown): Watershedss Wetland Management. http://www.water.ncsu.edu/watershedss/info/wetlands/manage.html#prot</ref>. Thus buffers can benefit the sustainable use of the MHP and should hence be established and/or protected. | A buffer typically consists of a band of vegetation along a wetland or water body, preferably natural habitat, but including previously altered, stable native or introduced species. A buffer can perform a variety of functions, which can improve the environmental condition of a watershed, such as sediment removal and erosion control, runoff reduction through infiltration, reduction of human impacts by limiting easy access as well as barrier to invasion of exotic species<ref>GALE, J.A. (unknown): Watershedss Wetland Management. http://www.water.ncsu.edu/watershedss/info/wetlands/manage.html#prot</ref>. Thus buffers can benefit the sustainable use of the MHP and should hence be established and/or protected. | ||
<br/> | <br/> | ||
| + | <br/> | ||
=== <br/>Eucalyptus vs. Indigenous Plants<br/> === | === <br/>Eucalyptus vs. Indigenous Plants<br/> === | ||
| − | Eucalyptus easily adapts to any soil and water condition, it is characterized by fast growth, high survival, long roots and hard leafs. Those features make it economically very beneficial. When it comes to watershed management, its negatives sides should be considered though: it does not only take a lot of nutrients and water and is hence a high competition to companion plants and decreases biodiversity, also soil erosion can occur which can negatively affect the [[ | + | |
| + | Eucalyptus easily adapts to any soil and water condition, it is characterized by fast growth, high survival, long roots and hard leafs. Those features make it economically very beneficial. When it comes to watershed management, its negatives sides should be considered though: it does not only take a lot of nutrients and water and is hence a high competition to companion plants and decreases biodiversity, also soil erosion can occur which can negatively affect the [[Causes_and_Features_of_Watershed_Degradation_related_to_MHP_Projects#Box_1|MHP’s performance]]. FAO thus recommends that large scale monocultures of eucalyptus plantations be excluded from watersheds, aforestation projects should avoid monocultures and the use of eucalyptus. The only way to include eucalyptus is to adopt it in agroforestry systems, but the proportion of each species should be planned out carefully<ref>SUNGSUMARN, K. (1993): Why Eucalyptus is Not Adopted for Agroforestry. In: Kashio, M. et al. (Hrsg.)(1996): Reports Submitted to the Regional Expert Consultation on Eucalyptus - Volume II. Bangkok: FAO Regional Office for Asia and the Pacific.</ref>. | ||
<br/> | <br/> | ||
| + | <br/> | ||
= Further Information<br/> = | = Further Information<br/> = | ||
*[[Portal:Hydro|Hydro Portal on energypedia]]<br/> | *[[Portal:Hydro|Hydro Portal on energypedia]]<br/> | ||
| − | *[[ | + | *[[Environment_Assessment_Related_to_Micro-hydro_Power_(MHP)_Projects_in_Ethiopia|Environment Assessment Related to Micro-hydro Power (MHP) Projects in Ethiopia]] |
| − | *[[ | + | *[[Environment_Assessment_and_Watershed_Action_Planning_Related_to_Micro_Hydro_Power_Projects_(MHPs)|Environment Assessment and Watershed Action Planning Related to Micro Hydro Power Projects (MHPs)]] |
| + | |||
<br/> | <br/> | ||
| + | <br/> | ||
= References = | = References = | ||
| + | |||
<references /><br/> | <references /><br/> | ||
| + | [[Category:Micro_Hydro]] | ||
| + | [[Category:Impacts_Environmental]] | ||
[[Category:Hydro]] | [[Category:Hydro]] | ||
| − | |||
Revision as of 14:31, 8 April 2015
Overview
The identification of appropriate mitigation and intervention techniques on the basis of the Environment Assessment is crucial for the implementation of a successful Watershed Action Plan in order to achieve a sustainable use of the catchment area and thus the MHP project.
Biophysical as well as political mitigation and intervention techniques are presented in this article.
Biophysical Measures
Gully Control
► Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Gully Control
Agro-forestry, Forage Development and Forestry
Soil Fertility Management and Biological Soil Conservation
Flood Control and Improved Drainage
Physical Soil and Water Conservation
Water Harvesting
► Micro-hydro Power (MHP) Projects - Mitigation and Intervention Techniques - Water Harvesting
Education and Training
► Watershed Action Planning related to Micro-hydro Power (MHP) Projects in Ethiopia - Training
Participatory Approach
Improving the Environmental Condition of the Catchment
Adetailed list of mitigation and intervention techniques and the respective application can be found in
► DESTA, L. ET AL. (2005): Part 1: Community Based Participatory Watershed Development. Addis Ababa: Ministry of Agriculture and Rural Development, pages 69 – 165
► DESTA, L. ET AL. (2005): Part 2: Community Based Participatory Watershed Development: Annex. Addis Ababa: Ministry of Agriculture and Rural Development, pages 43 - 48.
Fenced vs. Unfenced Springs / Wetlands
Springs and wetlands not only guarantee the discharge in dry season, also they have a great retention capacity during and after rains. Springs are sensitive areas that react to disturbances easily. Protection of springs and wetlands is thus crucial for the sustainable use of the MHP projects. Protection measurements might include fencing (to protect the areas from cattle step and thus soil compaction), protection of natural vegetation around the springs, protection of a natural humus layer (in order to sustain sufficient infiltration and thus groundwater recharge). Furthermore fencing can help to improve the water quality, since pollution due to agricultural and pastoral use can be prevented[1].
Buffered vs. Unbuffered Riverbanks / Wetlands
A buffer typically consists of a band of vegetation along a wetland or water body, preferably natural habitat, but including previously altered, stable native or introduced species. A buffer can perform a variety of functions, which can improve the environmental condition of a watershed, such as sediment removal and erosion control, runoff reduction through infiltration, reduction of human impacts by limiting easy access as well as barrier to invasion of exotic species[2]. Thus buffers can benefit the sustainable use of the MHP and should hence be established and/or protected.
Eucalyptus vs. Indigenous Plants
Eucalyptus easily adapts to any soil and water condition, it is characterized by fast growth, high survival, long roots and hard leafs. Those features make it economically very beneficial. When it comes to watershed management, its negatives sides should be considered though: it does not only take a lot of nutrients and water and is hence a high competition to companion plants and decreases biodiversity, also soil erosion can occur which can negatively affect the MHP’s performance. FAO thus recommends that large scale monocultures of eucalyptus plantations be excluded from watersheds, aforestation projects should avoid monocultures and the use of eucalyptus. The only way to include eucalyptus is to adopt it in agroforestry systems, but the proportion of each species should be planned out carefully[3].
Further Information
- Hydro Portal on energypedia
- Environment Assessment Related to Micro-hydro Power (MHP) Projects in Ethiopia
- Environment Assessment and Watershed Action Planning Related to Micro Hydro Power Projects (MHPs)
References
- ↑ HELVETAS (2005): Helvetas Wasser Fact Sheet: Quellen und Quellschutz.
- ↑ GALE, J.A. (unknown): Watershedss Wetland Management. http://www.water.ncsu.edu/watershedss/info/wetlands/manage.html#prot
- ↑ SUNGSUMARN, K. (1993): Why Eucalyptus is Not Adopted for Agroforestry. In: Kashio, M. et al. (Hrsg.)(1996): Reports Submitted to the Regional Expert Consultation on Eucalyptus - Volume II. Bangkok: FAO Regional Office for Asia and the Pacific.
