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1 Land use map of Rwanda Prepared during a workshop held in Butare, Rwanda at the CGIS centre, from the 22 nd of November until the 3 rd of december Dec 2010 in the framework of the Kagera TAMP project, implemented by FAO, funded by GEF

Land Use Map of Rwanda - Food and Agriculture · PDF file · 2017-11-28SCC-VI AGROFORESTRY MARA PROJECT, ... 8.7 Poverty ... Kagera Trans-boundary Agroenvironmental Management Programme

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1

Land use map of Rwanda

Prepared during a workshop held in Butare, Rwanda

at the CGIS centre,

from the 22nd

of November until the 3rd

of december Dec 2010

in the framework of the Kagera TAMP project,

implemented by FAO, funded by GEF

2

Workshop participants names (authors of the Rwanda maps are the member of the Rwanda team)

COUNTRY NAME INSTITUTE E-MAIL

RWANDA

Ernest Uwayezu CGIS NUR, HUYE (BUTARE) [email protected]

Elias Nyandwi CGIS NUR, HUYE (BUTARE) [email protected] [email protected]

Antoine Nsengiyumva Kagabo NATIONAL LAND CENTRE, KIGALI [email protected]

Theodomir Mugiraneza CGIS NUR, HUYE (BUTARE) [email protected]

Marie Christine Simbizi CGIS NUR, HUYE (BUTARE) [email protected]

Rachel Murekatete CGIS NUR, HUYE (BUTARE)

Jules Mutabazi ISAR, LIVESTOCK UNIT, KARAMA [email protected]

U. R. OF TANZANIA

Kipondya Winfrida

SCC-VI AGROFORESTRY KAGERA PROJECT, BUKOBA [email protected]

Godwin Safari Edmund Athanas

SCC-VI AGROFORESTRY MARA PROJECT, MUSOMA [email protected]

Frank Onesmo Mkiramwinyi

UKINGURU TRAINING INSTITUTE, MWANZA [email protected]

Elmens Kaboni

MINISTRY OF AGRICULTURE AND FOOD SECURITY, MWANZA [email protected]

UGANDA Dennis Babaasa

INSTITUTE OF TROPICAL FOREST CONSERVATION, BWINDI FOREST NATIONAL PARK [email protected]

Grace Nangendo WILDLIFE CONSERVATION SOCIETY, KAMPALA

[email protected] [email protected]

National Coordinator, Theobald Mashinga (2010), FAO

International Consultant: Dennis Babaasa

National Consultant: Ernest Uwayezu, CGIS NUR

Coordination of activities and facilitator Monica Petri, FAO

Kagera TAMP project contact: [email protected]

We thank the Nile Equatorial Lakes Subsidiary Action Program (NELSAP) of Nile Basin Initiative

(NBI), that provided a significant proportion of GIS inputs data used during the workshop. Input

data were prepared within the preparation of the « Monographie du bassin de la Kagera. Rapport su

le développement du bassin publiée » of the Kagera river basin transboundary water resources

management and development project of the Nile basin Initiative (NELSAP) in July 2008 in

collaboration with BRL Ingénierie.

We thanks Tim Robinson (FAO Senior Officer, NRC), Valentina Ercoli, (FAO Officer, NRC) and

Gianluca Franceschini (FAO Consultant) for the support during the preparation of livestock data.

The method used in this workshop has been developed within the project LADA FAO/UNEP GEF

and is available in the document: Freddy Nachtergaele, Monica Petri, 2011. Mapping Land Use

Systems at global and regional scales for Land Degradation Assessment Analysis. LADA technical

report ( http://www.fao.org/docrep/017/i3242e/i3242e.pdf ).

3

All intellectual property rights, including copyright, in the work performed under the

“Transboundary Agro-Ecosystem Management Programme for the Kagera River Basin” (thereafter

referred as “Kagera TAMP”) shall be vested in FAO, including without any limitations, the right to

use, publish, translate, sell or distribute, privately or publicly, any item or part thereof for non-

commercial purposes. FAO hereby grants to the delegated institution(s) of beneficiary country a

non-exclusive royalty-free license to use, publish, translate and distribute, privately or publicly, any

item or part of the work performed under Kagera TAMP for non-commercial purposes. Delegated

institutions are MINAGRI RAB, RNRA, REMA, GIS NUR, Kagera TAMP Districts, and Nile

Basin Initiative.

4

Index

Contents Index..................................................................................................................................................... 4 1. Introduction, Kagera TAMP project and national LADA method used at the Kagera basin scale . 5 2. Inputs, formats, scale, resolution and precision ............................................................................... 6 3. Africover re-classification................................................................................................................ 7

4. Validation of the land cover classes ................................................................................................. 9

5. Other data used to prepare the land use map ................................................................................. 12

5.1 Protected area ........................................................................................................................... 12 5.2 Classification of livestock statistical data ................................................................................ 13

5.2.1 Use of Agro – ecological zones of Rwanda as a base for livestock distribution .............. 13 5.2.2 Livestock intensity ............................................................................................................ 14

6. Land use map implementation ................................................................................................... 17

7. Land use map improvements ..................................................................................................... 17 8. Land use map database implementation .................................................................................... 19

8.1 Livestock natural region and livestock species .................................................................... 19 8.2 Annual rainfall ..................................................................................................................... 19

8.3 Annual temperature .............................................................................................................. 19

8.4 Elevation and slope .............................................................................................................. 19 8.5 Soil ....................................................................................................................................... 19 8.6 Population density ................................................................................................................ 22

8.7 Poverty ................................................................................................................................. 22

5

1. Introduction, Kagera TAMP project and national LADA method used at the Kagera basin scale

The Kagera TAMP project is funded through the Global Environment Facility (GEF) in partnership

and with co-funding from the governments, partner programmes and donors at country and regional

levels. The project is executed by the UN Food and Agriculture Organization (FAO). The project

goal is to adopt an integrated ecosystems approach for the management of land resources in the

Kagera basin that will generate local, national and global benefits including: restoration of degraded

lands, carbon sequestration and climate change adaptation and mitigation, protection of

international waters, agro-biodiversity conservation and sustainable use and improved agricultural

production, leading to increased food security and improved rural livelihoods.

Kagera Trans-boundary Agroenvironmental Management Programme is going to select its

intervention areas on the base of the more advanced technologies of definitions and assessment of

the land degradation and of the sustainable land management. The selection of most degraded zones

or of the areas with a higher impact of land degradation will provide the basis for the identification

of locations of the next project phases, particularly the implementation of the Farmer Field Schools.

This work will be realised in Rwanda, Uganda, and United Republic of Tanzania, and also in the

entire Kagera Basin (the workshop in Burundi was held from 9th

up to 16th

of November). The

method will be used fro the first time at a hydrographical basin scale.

The selection of intervention areas will be based on the method implemented by the project LADA

(FAO/UNEP GEF) that developed a national assessment method for the land degradation and

sustainable land management that has been tested in six countries (South Africa, Argentina, China,

Cuba, Senegal, Tunis). The method, very rapid, is composed by two main axes:

- the preparation of a land use systems (LUS) map by using all best available data,

- the preparation of the land degradation and sustainable land management map using the

method LADA WOCAT QM, that use the LUS as cartographic unit.

A workshop was organized by Kagera TAMP in Butare (Huye) between the 22nd

of November and

the 3rd

of December 2010 with the participation of GIS experts having different background

(agronomy, livestock, land cover, GRID, etc.) with the objective of preparing a LUS map of the

area. Data used are prepared by NELSAP (Nile Equatorial Lakes Subsidiary Action Program) in

2008 and have been provided to the Kagera TAMP team within the preparation of a Memorandum

of Understanding.

The present report give the complete description of the preparation of a land use map and also the

preparation of a national map of livestock intensity, needed as LUS input. The present method

allows the preparation of a multi-country land use map in two weeks with the work of 13 experts,

and is comparable to the continuous of 130 working days. Further to that, the LUS has been

validated with the support of GIS consultants.

The report details the work realised during the workshop describing the LUS preparation for

Rwanda.

6

2. Inputs, formats, scale, resolution and precision

Table 1 Land use systems data for map

Used for Name Year of

measure

Year / periodicity

of publication

Scale / resolution /

extent Format

Availability or copyright

Producer Metadata Unity of

measurements

Admin units RWA (District) 2006 - 1:250.000 Shp free MINALOC none classes

Land cover based ecosystsems

Africover 1999 2002 1:100.000 shp country FAO and

MINITERE www.africover.org

classes

Livestock density

Livestock statistics

2006 yearly Old

provinces (2001)

stats free National

Institute of Statistics

report heads per species

Livestock natural distribution regions

Agroecological zones

1980 - 1:250.000 shp free MINAGRI none classes

Protected areas

World database protected areas

2009 yearly 1:1.000.000 shp

(polygons) free UNEP

www.wdpa.org

classes

Elevation SRTM Hydrosheds

2000 2007 90 m GRID free NASA

Hydrosheds Hydrosheds.er.usgs.org

7

Table 2 Information on resolution, scale, format and precision

Resolution 90 mètres (basée sur le DEM SRTM)

Scale 1 : 250.000 based on the data (based on agroecological zones)

Format ESRI GRID

Précision In the tab general, insert the working directory

In the tab extent, select the analysis extent (probably “as …” the baseline

layer)

In the tab extent, Snap extent to (probably “as …” the baseline layer)

In cell size, select the cell size (probably “as …” the baseline layer).

Correction by using Generalization commands have been used as needed.

Validation Results are based on experience of the work group. Results are not validated.

3. Africover re-classification

The LUS map is based on land cover, which represents the ecosystems where that are used by

human being to establish the land use, or to obtain goods and services from an area. The LUS need

to be prepared over a very generalized land unit. The reclassification has been realised by using the

class name (LC_NAME) of the Aggregated Africover version.

The simplification took place in a participatory manner; with the collaboration of national experts

that use Africover in their regular work or that participated on Africover preparation. Thus, new

classes combining two or more Africover classes as summarized in the table below.

One more improvement has been done for the area alongside the Kivu Lake where Coffee and

Bananas plantations are the main crops and should be considered as perennial crop and not

seasonal. For deriving the abovementioned area, map algebra was used as a geo-processing tool.

The following conditions were proposed as input query:

To be at the elevation range of 1460 to 1540 metres. The later was selected from the DEM

Grid in order to delineate the eastern hillside of Kivu Lake. The motivation for choosing this

elevation range is attributed to the fact that the elevation value at lake level is 1460 whereas

its eastern hillside occupied by perennial crops has an estimated denivellation of 100m from

lake level;

That elevation range should be within districts bordering Kivu Lake (including Rubavu,

Rutsiro, Karongi and Nyamasheke) and

The previous land use type should be seasonal crops.

Table 3 Reclassification of Africover classes in Rwanda

LCNAME new_class

Combination of Shrub Plantation and Rainfed Herbaceous Crop (approx. 60-70% and

30-40%)

Forest Plantation

Forest Plantation - (Eucalyptus) - (or Pinus and Cypress)

Forest Plantation (Eucalyptus) or Pinus and Cypress (mixed unit with natural

vegetation or other) (field area approx. 60% polygon area)

Scattered (in natural vegetation or other) Forest Plantation (Eucalyptus) or Pinus and

Cypress (field density 20-40% polygon area)

Scattered (in natural vegetation or other) Shrub Plantation - Undifferentiated (field

density 20-40% polygon area)

Shrub Plantation - Undifferentiated (mixed unit with natural vegetation or other)

(field area approx. 60% polygon area)

8

Shrub Plantation - Undifferentiated

Combination of Forest Plantation and Rainfed Herbaceous Crop - Two crop per year

(approx. 30% each; remaining polygon surface natural vegetation)

Seasonal Crops

Combination of Rainfed Herbaceous Crop - Two crop per year - and Forest Plantation

(approx. 70-80% and 20%-30%)

Combination of Rainfed Herbaceous Crop - Two crop per year and Shrub Plantation

(approx. 40-60% and 20-40%; remaining Forest Plantation - (Eucalyptus) - (or Pinus

and Cypress))

Combination of Rainfed Herbaceous Crop - Two crop per year and Shrub Plantation

(approx. 40-60% and 20-40%; remaining natural vegetation)

Combination of Rainfed Herbaceous Crop and Forest Plantation (approx. 40-60% and

20-40%; remaining natural vegetation)

Combination of Rainfed Herbaceous Crop and Shrub Plantation (approx. 40-60% and

20-40%; remaining natural vegetation)

Combination of Shrub Plantation and Rainfed Herbaceous Crop - Two crop per year

(approx. 40-60% and 20-40%; remaining Forest Plantation - (Eucalyptus) - (or Pinus

and Cypress))

Combination of Shrub Plantation and Rainfed Herbaceous Crop - Two crop per year

(approx. 40-60% and 20-40%; remaining natural vegetation)

Irrigated Herbaceous Crop

Isolated (in natural vegetation or other) Forest Plantation (Eucalyptus) or Pinus and

Cypress (field density 10-20% polygon area)

Isolated (in natural vegetation or other) Rainfed Herbaceous Crop - Two Crop Year -

(field density 10-20% polygon area)

Isolated (in natural vegetation or other) Rainfed Herbaceous Crop (field density 10-

20% polygon area)

Post Flooding Herbaceous Crop (mixed unit with natural vegetation or other) (field

area approx. 60% polygon area)

Post Flooding Herbaceous Crop

Rainfed Herbaceous Crop - Two Crop Year (mixed unit with natural vegetation or

other) (field area approx. 60% polygon area)

Rainfed Herbaceous Crop

Rainfed Herbaceous Crop -Two Crop Year

Scattered (in natural vegetation or other) Rainfed Herbaceous Crop - Two Crop Year

- (field density 20-40% of polygon area)

Scattered (in natural vegetation or other) Rainfed Herbaceous Crop (field density 20-

40% of polygon area).

Closed Herbaceous Vegetation

Grasslands Savannah (shrub or tree and shrub)

Sparse Herbaceous Vegetation

Rice Fields Irrigated Crops

Closed Shrubs

Natural_forest

Closed Trees

Multilayered Trees Broadleaved Evergreen

Open Broadleaved Deciduous Trees

Open Shrubs

Combination of Banana Plantation and Rainfed Herbaceous Crop (approx. 60-70%

and 30-40%) Perennial Crops

Tea Plantation

Closed Herbaceous Vegetation

Savanna

Open Shrubs (on temporarily flooded land - fresh water)

Open Shrubs

Savannah (shrub or tree and shrub)

Sparse Herbaceous Vegetation

Water Bodies Surface water

Urban And Associated Areas Urban and built up areas

Closed Herbaceous Vegetation On Permanently Flooded Land - Fresh Water

Wetland Closed Herbaceous Vegetation With Sparse Trees in Temporarily Flooded Land -

Fresh Water

9

4. Validation of the land cover classes

The validation was prepared by using the following GIS data layers obtained from Rwanda Natural

Resource Authority/Land and Mapping Department: Forest Plantations

Protected wetlands

Wetlands

Irrigated crops

Vegetation and land cover

Natural forests

Built-up area

Agriculture zones Settlements

Also, the validation team was able to use the Land and Mapping Department office, the recent

(2008), high resolution aerial photographs (25 cm) for areas where the land cover type was not clear

or confusing. We therefore did not find it necessary to make field trips to validate the land cover

map.

Main modification of the land cover classes are presented in table 4.

Table 4 Changes made to the Land Cover map of Rwanda during validation exercise

Administrative Unit (former

Provinces)

Changes made to Land Cover

Classes

Remarks

Kigali More area under Built up areas

mapped

Kigali City has greatly expanded

East Woodland ecosystem class

introduced

Were previously classified as

Natural Forest in the Land Cover

map. We reclassified them as

Woodlands as they are mostly

dominated by nearly same size/age

Acacia trees and are not layered like

the natural forests. Occur along river

courses and in the south in Bugesera

Grassland ecosystems removed These areas have same classification

in Africover map as savanna. The

grassland ecosystems were therefore

merged with savanna

More Built up Areas mapped Large settlements especially in the

north east were lacking in the Land

Cover map

More areas under Perennial crops

mapped

Perennial crops especially bananas

and coffee are being adopted,

especially in the south east and north

east eating up areas that used to be

under savanna and/or seasonal crops

More areas under Seasonal crops

mapped

The Savanna areas have been

reduced in recent past by converting

them to seasonal crops

More areas under Forest Plantations

mapped

Because majority of the individual

forest plantations are small in area,

they are normally not mapped in low

resolution maps. But because they

are many and cover a wider

landscape

More areas of Perennial crops

mapped

Areas under pyrethrum plantations,

and tea outside the irrigated areas

10

had not been mapped

More areas under Forest plantation

mapped

Because majority of the individual

forest plantations are small in area,

they are normally not mapped in low

resolution maps. But because they

are many and cover a wider

landscape

North Protected wetlands mapped Protected wetlands were not

originally mapped. There is a recent

Government policy to protect

wetlands that had not yet been

drained for agriculture

Grassland ecosystems removed Areas classified as grasslands were

successional stages of natural forest

or areas under herbs/shrubs in forest

plantations that were yet to be

planted or areas under fallow or

uncultivated areas in seasonal crops

ecosystem

More areas under Forest plantation

mapped

Because majority of the individual

forest plantations are small in area,

they are normally not mapped in low

resolution maps. But because they

are many and cover a wider

landscape

West More areas of Perennial crops

mapped

Plantations of coffee, and some

bananas are being established,

especially along the shores of Lake

Kivu

Protected crops class removed These were areas that had been

cultivated within the boundaries of

protected areas like Gishwati forest

but now are being restored to natural

forest or forest plantation

More areas under Forest plantation

mapped

Because majority of the individual

forest plantations are small in area,

they are normally not mapped in low

resolution maps. But because they

are many and cover a wider

landscape

More area under Built up areas

mapped

Settlements and towns have greatly

expanded e.g. Gisenyi

South More areas under Forest plantation

mapped

Because majority of the individual

forest plantations are small in area,

they are normally not mapped in low

resolution maps. But because they

are many and cover a wider

landscape

More areas under Perennial crops

mapped

Banana plantations are being

established

A map of reclassified land cover of Rwanda at 1/100000 was prepared by local experts. Ten (10)

new classes were created as shown on the figure below.

11

Figure 1Reclassified land cover map

12

5. Other data used to prepare the land use map

5.1 Protected area

The protected areas were derived from the World database of protected areas, 2008.

Figure 2 Rwanda protected areas

13

5.2 Classification of livestock statistical data

Available livestock data of 2003 (2008) have been used as baseline.

Table 5 Livestock heads in Rwanda in 2003

NAME/Province Cattle Sheep Goats Pigs

Butare 85396 8270 310340 43391

Byumba 76392 110885 193543 10294

Cyangugu 60092 29068 169889 53871

Gikongoro 69674 82171 134606 68355

Gisenyi 49350 123299 290140 93436

Gitarama 165416 42068 213160 60142

Kibungo 62581 3118 380120 19988

Kibuye 66358 76327 223620 38393

Kigali Ngari 120209 42000 386029 41505

Kigali Ville 0 0 0 0

Ruhengeri 84152 174053 188988 77108

Umutara 282559 4108 165363 21048

In table above, Kigali as the capital city was not covered by the inventory.

Those data has been converted to tropical livestock units (TLU) using the same conversion factors

as defined by NBI-NELSAP for the Kagera basin: cattle 0.75, goats 0.1, sheep 0.1, pigs 0.2. With

the aim of having a data that is comparable between species and districts of different dimension, the

results have been calibrated basing on extent, obtaining an indication of TLU/km2

Table 6 Tropical livestock units (TLU) per Km2

NAME/Province Cattle_TLU/km2 Sheep_TLU/km

2 Goats_TLU/km

2 Pigs_TLU/km

2

Butare 64047 827 31034 8678.2

Byumba 57294 11088.5 19354.3 2058.8

Cyangugu 45069 2906.8 16988.9 10774.2

Gikongoro 52255.5 8217.1 13460.6 13671

Gisenyi 37012.5 12329.9 29014 18687.2

Gitarama 124062 4206.8 21316 12028.4

Kibungo 46935.75 311.8 38012 3997.6

Kibuye 49768.5 7632.7 22362 7678.6

Kigali Ngari 90156.75 4200 38602.9 8301

Kigali Ville 0 0 0 0

Ruhengeri 63114 17405.3 18898.8 15421.6

Umutara 211919.3 410.8 16536.3 4209.6

5.2.1 Use of Agro – ecological zones of Rwanda as a base for livestock distribution

Livestock map using statistics per administrative unit does not reflect the realistic spatial

distribution. Using our experience we managed to improve spatial pattern, distribution of livestock

14

using agro –ecological zones of Rwanda. The agro –ecological zones maps has been created by

Ministries of Agriculture (MINAGRI) in 80’s at a scale of 1/250 000 with ten classes as illustrated

in the figure bellow.

Figure 3 Agro-ecological zones of Rwanda defined by MINAGRI

5.2.2 Livestock intensity

The livestock map has been prepared following 2 phases:

Creating a density map of livestock distribution per region using tropical livestock unit

based on 2003 statistics

Creating livestock intensity map based on livestock map per administrative unit and spatial

distribution using agro-ecological zones judging using our experience.

The scoring table was created as follow:

Table 7 Scoring livestock dominance per province in 2003

les savanes de l'Est les hautes terres de

Burebuka les cones et hautes plaines

volcaniques les cretes et plateaux

bordant les savanes de l'Est

Province CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS

Butare

Byumba y y y Y Y Y

Cyangugu

Gikongoro

Gisenyi y y

Gitarama y y

Kibungo y y Y y

15

Kibuye

Kigali Ngari Y Y y

Kigali Ville

Ruhengeri y y

Umutara Y y y Y Y

la crete Zaire-Nil le Plateau Central le bord du lac Kivu les hautes terres de

Burebuka

Province CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS

Butare y Y

Byumba Y Y Y

Cyangugu Y Y Y

Gikongoro Y Y Y Y

Gisenyi Y y y y Y y

Gitarama y Y Y

Kibungo

Kibuye Y y y Y

Kigali Ngari y

Kigali Ville

Ruhengeri y y y

Umutara

le Mayaga et Bugesera

peripheriques l'arriere pays de Cyangugu la Plaine de Bugarama

Province CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS CATTLE GOATS SHEEP PIGS

Butare Y y

Byumba

Cyangugu y y y

Gikongoro

Gisenyi

Gitarama Y Y

Kibungo y y

Kibuye

Kigali Ngari Y Y

Kigali Ville

Ruhengeri

Umutara

16

Figure 4 Livestock intensity map (source data also include livestock statistics)

17

6. Land use map implementation

The baseline for land use preparation is land cover. The preparation of land use has been prepared

using livestock intensity, protected areas and wetlands areas. Data have been classified using the

conditional command (“CON”) of ArcGIS Spatial Analyst. In total twenty seven (27) major classes

for land use systems have been created as shown in the table below.

Table 8 Main land use systems

Code/Value Land Use Classes

1 Protected natural forest

3 Natural forest with livestock

4 Protected forest plantation

6 Forest plantation with livestock

7 Protected Savana

8 Savana with high livestock

9 Savana with moderate livestock

10 Protected Grassland

12 Grassland with livestock

13 Protected wetland

15 Wetland with livestock

16 Crop in protected area

18 Perennial Crops with livestock

19 Seasonal Crops with high livestock

20 Seasonal Crops with moderate livestock

22 Irrigated Crops with livestock

23 Protected Surface water

25 Surface water with other uses

27 Urban area

Land use classes qualified as having:

High livestock intensity were those having a threshold of above forty seven (47) tropical

livestock units per km2,

Moderate livestock intensity were those having a threshold of below forty seven (47)

tropical livestock units per km2,

No livestock

7. Land use map improvements

The land use map is needed in the second part of the LADA (FAO/UNEP GEF) method, that

include the assessment of the land degradation and of the sustainable land management practices.

This exercise is realised using the participatory method LADA WOCAT QM throughout the

involvement of local experts. During the assessment LUS units are calibrated and improved basing

on participants suggestion. The final LUS map is presented in Figure 5.

18

Figure 5 Land Use System Map of Rwanda

19

8. Land use map database implementation

The database will be utilized during land degradation and sustainable land management assessment

as supporting material of the LADA WOCAT QM method. It gives additional information for the

groups of assessment. The use of the GRID formal allows converting all data to the baseline

resolution. The list of input data is available in table 10.

8.1 Livestock natural region and livestock species

The map of livestock region was prepared basing on the description in chapter 4.2. In the

preparation of the land use map, the carte has been used as input. With a slight modification and

following the same method than is chapter 4.2, the map can list the dominant livestock species. The

groups of dominant livestock species are the following:

Cattle and goats

Sheep

Cattle, sheep and goats

Sheep and pigs

Cattle and sheep

Goats and pigs

Cattle

Goats

8.2 Annual rainfall

The annual average rainfall amount is calculated by summing up monthly values downloaded from

the World Clim database, published in 2005. Although the data is at 30 arc seconds resolution, the

data is considered the best available to have an indicative representation of the rainfall of the area.

The data is presented in Figure 6.

8.3 Annual temperature

The annual temperature range is calculated from data downloaded from the World Clim database,

published in 2005. Although the data is at 30 arc seconds resolution, the data is considered the best

available to have an indicative representation of the rainfall of the area. The data is presented in

Figure 6.

8.4 Elevation and slope

The elevation (meters) at a resolution of 90 meters is obtained using SRTM 2000 data included in

the Hydrosheds database published in 2007. The slope (degrees) is interpolated from the same

dataset. The data are presented in Figure 7.

The elevation map use the following elevation classes in the database: 900-1000,1000-1400,1400-

1800,1800-2200,2200-3000,> 3000. The slope classes are: 0-2,2-8,8-16,16-32,>32.

8.5 Soil

The soil map is downloaded from the Harmonized would soil database with a resolution of 30 arc

seconds and is presented in Figure 8.

20

Table 8 Input data for LUS database preparation

Used for Name Year of

measure

Year / periodicity

of publication

Scale / resolution

/ extent Format

Availability or

copyright Producer Metadata

Unity of measurements

Admin units RWA (District) 2006 - 1:250.000 Shp free MINALOC none classes

Temperature Wordclim - 2005 30 arc

seconds GRID free www.worldclim.org www.worldclim.org degree

centigrads

Livestock density

Livestock statistics

2006 yearly Old

provinces (2001)

stats free National Institute

of Statistics report

heads per species

Livestock natural distribution regions

Agroecological zones

1980 - 1:250.000 shp free MINAGRI none classes

Rainfall Wordclim - 2005 30 arc

seconds GRID free www.worldclim.org www.worldclim.org mm

Elevation SRTM Hydrosheds

2000 2007 90 m GRID free NASA

Hydrosheds Hydrosheds.er.usgs.org m

Slope SRTM Hydrosheds

2000 2007 90 m GRID free NASA

Hydrosheds Hydrosheds.er.usgs.org degree

Soil HWSD 2008 2008 30 arc

seconds GRID free

FAO

IIASA

ISRIC

ISSCAS

JRC

http://www.iiasa.ac.at/Research/LUC/External-World-soil-database/HTML/ -

Population density

population statistics

2002 yearly - stats country ? inhabit /sq km

Poverty Poverty heard index

2005-6 - - stats free

National

institute of

statistics of

Rwanda

none EICV

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Figure 6 Annual rainfall and temperature range

Figure 7 Elevation and slope

22

Figure 8 Soil map

8.6 Population density

Population data (inhabitants per districts) are available from the national census for the year 2002.

To be able to compare data between district, the population density has been calculated by dividing

the population for the area in square kilometres. The list of classes used in the database is the

following: 55-100,100-300,300-500,500-800,>800. The map is presented in figure 9.

8.7 Poverty

In 2007 the National institute of statistics of Rwanda published the report “EICV poverty analysis

for rwanda's economic development and poverty reduction strategy” including the assessments

derived from the Enquete Intégrale sur les Conditions de Vie des ménages de Rwanda, that provide

as a result the indicator Poverty headcount by province (EICV2). From this report, the values in

percentages have been converted to the map presented in figure 9. The classes used in the map are:

20-30,30-60,60-65, >65.

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Figure 9 Map of socio-economical indicators including population density and poverty