Trenches combined with living hedges or grass lines Rwanda - Imiringoti

Similar documents
Radical Terraces Rwanda - Amaterasi y'indinganire

Stone lines Uganda - Ennyiriri z'amayinja eziziyiza ettaka okutwalibwa enkuba (Luganda)

Bench terraces on loess soil China - 土坎梯田, 梯地

Zero grazing Uganda - Okurisiza hamwe

Green cane trash blanket Australia - Trash blanket

Multi-Storey Cropping Philippines - Maramihang Pagtatanim or Planting in Great Numbers

Crop rotation with legumes Chile - Rotación de cultivos con leguminosas (Spanish)

Improved grazing land management Ethiopia - Gitosh masheshal

Olive tree plantations with intercropping Morocco - Plantations d olivier avec cultures intercalaires (Fr), Jnane Zitoune (Ar)

Natural forest conservation using apiaries Tanzania, United Republic of - Utunzaji misitu kwa kufuga nyuki (swahili),

Classification. Rice husks as well as empty seeds are pyrolised and used as a soil amendment in the rice seed beds and the vegetable gardens.

EFFECTIVE CONSERVATION PRACTICES FOR THE CULTIVATION OF SLOPELANDS

Enhancing sustainable production adaptations for recovery in a degraded environment

Watershed BMPs. Notes from NRCS online site on BMPs. Focus on key BMPs

Rehamna landscape restoration project

Conservation Practices. Conservation Choices. These five icons will show the benefits each practice offers... 6/4/2014

Popular Kheti. Volume-2, Issue-3 (July-September), 2014 Available online at popularkheti.info ISSN:

African Organic Agriculture Manual Booklet Series No. 3 Soil and water conservation HOW DO I PROTECT THE SOIL NUTRIENTS AND WATER FROM LOSS?

FACTSHEET INTRODUCTION. help rebalance the water cycle, mitigate the effects of climate change and improve human health and livelihoods.

Degradation of the resource Fertility loss Organic matter Tilth degradation. Water quality Sediment Nutrients

Appendix I New Zealand Land Use Capability Classification

From the Ground Up- Field Soil Considerations

Agriculture and Society: Part II. PA E & E Standards 4.4

The Science of Maryland Agriculture

Acceptability High Effectiveness High Affordability High Timing / Urgency High

GLASI GLASI. Priority Subwatershed Project. Great Lakes Agricultural Stewardship Initiative

Catchment Approach. Problem, objectives and constraints. Kenya

The Green Liver System : eco-friendly water purification Brazil - Fitorremediação (Portuguese)

Status of climate change adaptation in agriculture sector for Lao PDR.

Watercourses and Wetlands and Agricultural Activities

Chapter 9: Soil and Agriculture

The Vetiver System, a biological solution for development and conservation at Madagascar

Grassed Waterway Improvement and Gully Restoration

LUS mapping LD/SLM assessment

VETIVER SYSTEM. Application under Kuwaiti Environment. Dr. Paul Truong Veticon Consulting Brisbane, Australia

Water Catchment management through a 3R approach- Case of RWAMBU Catchment-Western Uganda

Recommended Resources: The following resources may be useful in teaching this lesson:

The water resources of Eastern and Southern. Some Interventions for Managing Water for Agriculture in Eastern and Southern Africa

Unit E: Basic Principles of Soil Science. Lesson 7: Understanding Soil Erosion and Management Practices

Conservation Practices for Water Quality: Sediment & Nutrient Control. Trap Sediments/Trap Nutrients on the Field. Improve Soil Health.

Soil Degradation. Lesson Plan NRES B2-9

Assessment of the Role of Trees on Farmland in Soil Conservation and Household Welfare in Rwanda.

REMOTE SENSING AND GIS FOR INTEGRATED LAND MANAGEMENT: CASE OF INDIA

ROADS: OPERATION AND MAINTENANCE

Assessing the Carbon Benefits of Improved Land Management Technologies

PROBLEMS WITH CASSAVA PRODUCTION IN THE UPLANDS OF SOUTHERN MINDANAO

Deatiled Project Report Vamanapuram IWMP 1

CLIMATE SMART AGRICULTURE

Of vital importance..

OVERVIEW OF RUSLE 2 DICK WOLKOWSKI DEPT. OF SOIL SCIENCE UW-MADISON

Dryland Degradation by Wind Erosion

USING TITHONIA AS A FERTILISER

Use of household ponds for garden irrigation and fish production.

Appendix D. Erosion Management Sub- Plan

Sediment and Erosion Control Plan (SECP) Template

Sara J. Scherr, EcoAgriculture Partners Navigating the Global Food System in a New Era IAMA, Boston, June 21, 2010

Analysis of Effectiveness of Ohio NRCS Practice Standards in Addressing Five Leading Causes of Water Quality Impairment

SLOPE MANAGEMENT FOR SUSTAINABLE AGRICULTURE IN THE UPLANDS

Agroforestry Research for Development in Shifting Cultivation Areas of Laos.

Erosion, Erosion, Everywhere

2-16 EROSION, SEDIMENT & STORM WATER CONTROL REGULATIONS APPENDIX B1

Grower Survey of Best Management Practices (BMPs)

Soil and farm practices data concerning the case study Svratka were collected according to questionnaire 1 by the expert on soil protection.

Papua New Guinea LNG Project. Environmental and Social Management Plan Appendix 11: Reinstatement Management Plan PGGP-EH-SPENV

SOIL AGRODIVERSITY AN ASPECT OF FARMERS MANAGEMENT OF BIOLOGICAL DIVERSITY

Conservation Practices for Landlords There is growing concern over the possible

Role of Soils in Water Quality. Mike Marshall Extension Associate Texas A&M-Institute of Renewable Natural Resources

Terraces in Africa. Typology, efficiency, limits & improvements. By Eric Roose

World Vision MUS Programming: a few minute review. Ron Clemmer WASH Sr. Technical Advisor - WVUS January 20, 2012

3.3 Soil Cultivation and Tillage

State of Agriculture in the Uplands of Southern Mindanao

LOSS AND RUNOFF. Background. 2 Soil Loss and Runoff

Reservoir age, increasing human population,

Pu Wang Department of Natural Resources Cornell University

Water Erosion in Slovakia - Problems and Solutions

East African PLEC General Meeting Arusha, Tanzania, 26-28, November, Household Diversity in the Smallholder farms of Nduuri, Embu, Kenya.

Greening Agriculture Policies and Laws

This presentation is sponsored by the Beginning Farmer and Rancher Development Program SUSTAINABLE AGRICULTURE

or 1

National Ecosystems and Landscapes Restoration Program of El Salvador

Soil Health Research Landscape Tool, v Data Dictionary Soil Health Institute 12/21/2016

Enhancing forest livelihoods in Uganda to advance REDD+

Nutrient Management in. A presentation to the West Metro Water Alliance

METROPOLITAN UTILITIES DISTRICT No Page: 1 of 10

Maitland Valley WATERSHED

Background for: Upper Piddle Headwaters

ENVS 435: Watershed Management

FACTSHEET: Grow Agriculturally Productive Buffers

Gray s Creek. Gray s Creek

Conservation. Conservation Practice. Cover 327. What is it? How it Works. Which Resource Concerns? Where it Works Best

V. Eligible Practices A. Cost-Share Practices

WATERSHED. Maitland Valley. Report Card 201

Challenges of Maintaining the Terraces in the Highlands

Local Government Commission California Adaptation Forum

Controlling runon and runoff:

Calculating Soil Loss

Very slight to negligible limitations no special land management practices required.

Overall Instructions

Sediment Management Goals and Management Practices for Strawberries

Domestic adaptation to climate change in Rwanda

Transcription:

Trenches combined with living hedges or grass lines Rwanda - Imiringoti Trenches combined with living hedges or grass lines are slow-forming terraces to control soil erosion by changing the length of the slope and progressively reducing the slope gradient; he slope steepness decreases progressively by hydric and tillage erosion. Trenches combined with living hedges or grassed lines are less labour-intensive method that is practiced in the highlands of Rwanda. The method involves digging trenches which have grass-stabilized banks, or simply planting grass strips and vegetative barriers across the slope to reduce runoff. This method, locally referred to as progressive terracing, is more adaptable by individual farmers across the country. In the study conducted by Kagabo et al. (2013) in the highlands of Buberuka Region of Rwanda, it was noted that net increment in yields and returns on investment increased with the age of terraces, since the capital costs of terracing were easily recovered. These terraces also showed more resilience, some being over 30 years old and still effective. Along the contour band, soil from the upper parts of the slope is removed and deposited above by creating a series of discontinuous trenches in order to extend the flat terrain. Over 5-10 years, the terraces become enlarged and form a terrace along the contour, such that the slopes are transformed over time into level bench terraces (but never %). The main purpose of this technology is to reduce runoff and soil erosion on the slope and to improve soil quality and soil moisture retention. Grass strips or living hedgerows are intended to both trap sediments and facilitate the slow formation of terraces. The establishment of trenches combined with living hedges or grassed lines is less labor intensive and requires less skilled labor. Regular maintenance banks on which living hedges are planted, to seasonally stream living hedges to minimize the competition of nutrients and water with plants. To efficiently use these terraces it is advisable to introduce intensive and rentable cropping systems or agroforestry with fruits and forage trees. This technology was reported to be very resilient as trenches combined with living hedges or grassed lines of 20+ year old are still effective in controlling soil erosion. However, the soil quality on these formed terraces between alleys does not homogenize 100% over the course of time. Large soil fertility gradients with marked spatial difference in both soil quality and crop yield from their upper parts downwards of the terraces is observed. The soil in the lower parts of the terraces showed as much as 57% more organic carbon content and 31% more available phosphorous than the soil in the upper parts of the terraces (Kagabo et al. 2013). left: Landscape view of the anti-erosion trenches and grass lines (Photo: Ngenzi Guy) right: Detailed view of trench combined with grass line (Photo: Kagabo Desire and Ngenzi Guy) Location: Rwanda Region: Kamonyi District (Southern Province) Technology area: 10-100 km2 Conservation measure: vegetative, structural Stage of intervention: mitigation / reduction of land degradation Origin: Developed Government, 10-50 years ago Land use type: Cropland: Annual cropping Cropland: Tree and shrub cropping Land use: Grazing land: Extensive grazing land (before), Cropland: Annual cropping (after) Climate: subhumid, tropics WOCAT database reference: T_RWA002en Related approach: Top down approach (A_RWA001en) Compiled by: Desire Kagabo, Not a member of an institution Date: 2014-07-04 Contact person: Desire Dr Kagabo, Rwanda Agriculture Board, Rwanda, (+250)788769080, desirekagabo@yahoo.com Classification Land use problems: - Soil erosion, water contamination due to sediment loads, decrease of soil fertility and soil depth, loss of vegetation cover (expert's point of view) Soil erosion, contamination of water (the turbidity of water is high) therefore the domestic use of water is a problem. (land user's point of view)

Land use Climate Degradation Conservation measure Annual cropping Tree and shrub cropping Grazing land: Extensive grazing land (before) Cropland: Annual cropping (after) rainfed rainfed subhumid Soil erosion by water: loss of topsoil / surface erosion vegetative: Grasses and perennial herbaceous plants structural: Graded ditches / waterways (to drain and convey water) Stage of intervention Origin Level of technical knowledge Prevention Mitigation / Reduction Rehabilitation Land users initiative Experiments / Research Externally introduced Other: Government: 10-50 years ago Agricultural advisor Land user Farmer representive Main causes of land degradation: Direct causes - Human induced: deforestation / removal of natural vegetation (incl. forest fires) Direct causes - Natural: other natural causes, Steep slopes in many cases are over 60% Indirect causes: population pressure Main technical functions: - control of concentrated runoff: retain / trap - reduction of slope length - improvement of topsoil structure (compaction) - increase of infiltration - sediment retention / trapping, sediment harvesting Secondary technical functions: - control of concentrated runoff: impede / retard - reduction of slope angle Environment Natural Environment Average annual rainfall (mm) Altitude (m a.s.l.) Landform Slope (%) > 4000 mm 3000-4000 mm 2000-3000 mm 1500-2000 mm 1000-1500 mm 750-1000 mm 500-750 mm 250-500 mm < 250 mm > 4000 3000-4000 2500-3000 2000-2500 1500-2000 1000-1500 500-1000 100-500 <100 plateau / plains ridges mountain slopes hill slopes footslopes valley floors flat gentle moderate rolling hilly steep very steep Soil depth (cm) 0-20 20-50 50-80 80-120 >120 Growing season(s): 150 days (September February), 120 days (March July) Soil texture: medium (loam) Soil fertility: medium Topsoil organic matter: medium (1-3%) Soil drainage/infiltration: good Soil water storage capacity: medium Ground water table: 5-50 m Availability of surface water: poor / none Water quality: poor drinking water Biodiversity: medium Tolerant of climatic extremes: temperature increase, seasonal rainfall decrease, wind storms / dust storms, droughts / dry spells, decreasing length of growing period Sensitive to climatic extremes: seasonal rainfall increase, heavy rainfall events (intensities and amount), floods

Human Environment Cropland per household (ha) <0.5 0.5-1 1-2 2-5 5-15 15-50 50-100 100-500 500-1,000 1,000-10,000 >10,000 Land user: Individual / household, Small scale land users, common / average land users, men and women Population density: 50-100 persons/km2 Annual population growth: 2% - 3% Land ownership: individual, titled Land use rights: individual Water use rights: open access (unorganised) Relative level of wealth: poor, which represents 75% of the land users; 75% of the total area is owned by poor land users Importance of off-farm income: less than 10% of all income: Access to service and infrastructure: low: technical assistance, employment (eg off-farm), energy, roads & transport; moderate: education, drinking water and sanitation, financial services; high: health, market Market orientation: subsistence (self-supply) Technical drawing Trenches are dug in trapezoidal shape with 40 cm of height, 30 cm of base length and 50 cm of top lengths. An empty space of 40 cm is left between two consecutive trenches along a contour line. (Kagabo Desire and Guy Ngenzi) Implementation activities, inputs and costs Establishment activities - Cuttings - Transport - Planting - Identification of contour lines, digging of trenches and grass planting on risers Establishment inputs and costs per ha Inputs Costs (US$) % met by land user Labour 381.25 100% Equipment - Hand hoe 125.00 100% TOTAL 506.25 100.00% Maintenance/recurrent activities - Weeding - Manure application and transportation - Grass streaming - Clearing the ditches by removing piled up sediments. Maintenance/recurrent inputs and costs per ha per year Inputs Costs (US$) % met by land user Labour 33.00 100% Equipment - Hand hoe 5.00 100% TOTAL 38.00 100.00% Remarks: The most determining factor affecting the cost is labor (the cost of labor increases with the nature of the soil structure as well as with the land steepness. The cost of labor is estimated based on land steepness, soil structure (deep, gravel or shallow soils). Land steepness defines the spacing between anti-erosion ditches hence affecting the cost of labor. Similarly, the soil structure (deep, gravel or shallow soils) defines the size of labor to be used per hectare. Assessment

Impacts of the Technology Production and socio-economic benefits increased crop yield increased fodder production Socio-cultural benefits conflict mitigation improved conservation / erosion knowledge Ecological benefits reduced surface runoff reduced soil loss improved harvesting / collection of water increased soil moisture reduced hazard towards adverse events improved soil cover Off-site benefits Production and socio-economic disadvantages increased labour constraints loss of land Socio-cultural disadvantages Ecological disadvantages Off-site disadvantages reduced downstream siltation reduced damage on neighbours fields Contribution to human well-being / livelihoods Increase in agricultural production has contributed to income generation and provide needed school fees Benefits /costs according to land user Benefits compared with costs short-term: long-term: Establishment neutral / balanced very positive Maintenance / recurrent slightly negative very positive Acceptance / adoption: 100% of land user families (207 families; 100% of area) have implemented the technology voluntary. There is strong trend towards (growing) spontaneous adoption of the technology. 100% of farmers has adopted the technology Concluding statements Strengths and how to sustain/improve Weaknesses and how to overcome Mitigation of land degradation due to soil erosion Continuous sensitization and enforcement by government to land users to stabilize the technology. Increased crop productivity Continuous training from government and give all basic necessary support services to land users Increased fodder production technology by land users Proper maintenance of the It requires a lot of physical energy, elderly people can't afford Help each other through communal work (umuganda) Labor costs Land users with less financial means should join their efforts by working together It is hard to implement mainly by older and poor land users It is required to offer communal support or financial support from development partners To prevent soil erosion Grasses provide mulching contour lines Maintenance of contour lines Proper maintenance of grasses on

Copyright (c) WOCAT (2014)