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<strong>Assessment</strong> <strong>of</strong> <strong>the</strong> <strong>biological</strong><br />

<strong>values</strong> <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong><br />

<strong>types</strong> <strong>in</strong> <strong>the</strong> East Usambara<br />

Mounta<strong>in</strong>s <strong>of</strong> Tanzania<br />

By Charles Leonard, Moses Mwangoka, Victor Mkongewa,<br />

Nike Doggart and He<strong>in</strong>i Vihemäki<br />

Dar es Salaam<br />

October 2010


Cover photographs by Charles Leonard From left to right: 1. a sugarcane farmplot that was started<br />

to be harvested with a forest patch on <strong>the</strong> background 2.a photo-mosaic <strong>of</strong> tea field with forest<br />

patch and human settlements<br />

© Tanzania Forest Conservation Group<br />

Suggested citation:<br />

Leonard, C., M. Mwangoka, V. Mkongewa, N. Doggart, and H. Vihemäki (2010) <strong>Assessment</strong> <strong>of</strong><br />

<strong>the</strong> <strong>biological</strong> <strong>values</strong> <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s <strong>of</strong> Tanzania.<br />

TFCG Technical Paper No. 23. DSM, Tz. 1 – 91 pp.


CONTENTS<br />

ABBREVIATIONS AND ACRONYMS ................................................................................ 1<br />

ACKNOWLEDGEMENTS ................................................................................................... 2<br />

1) INTRODUCTION ...................................................................................................... 3<br />

1.1 BACKGROUND TO THE PROJECT ................................................................................ 3<br />

1.2 REPORT STRUCTURE ............................................................................................... 3<br />

1.3 AN OVERVIEW OF THE EAST USAMBARA MOUNTAINS .................................................. 3<br />

2) BOTANICAL SURVEYS .......................................................................................... 5<br />

2.1 INTRODUCTION ........................................................................................................ 5<br />

2.2 METHODS ............................................................................................................... 5<br />

2.3 RESULTS ................................................................................................................ 6<br />

2.4 DISCUSSION .......................................................................................................... 14<br />

3) TRANSECT WALKS .............................................................................................. 22<br />

3.1 INTRODUCTION ...................................................................................................... 22<br />

3.2 METHODS ............................................................................................................. 22<br />

3.3 RESULTS .............................................................................................................. 22<br />

3.4 DISCUSSION .......................................................................................................... 22<br />

4) BIRDS .................................................................................................................... 23<br />

4.1 INTRODUCTION ...................................................................................................... 23<br />

4.2 METHODS ............................................................................................................. 23<br />

4.3 SAMPLING INTENSITY ............................................................................................. 23<br />

4.4 RESULTS .............................................................................................................. 24<br />

4.5 DISCUSSION .......................................................................................................... 27<br />

4.5.3 HABITAT ASSOCIATION ...................................................................................... 29<br />

5) MAMMALS ............................................................................................................. 30<br />

5.1 INTRODUCTION ...................................................................................................... 30<br />

5.2 METHODS ............................................................................................................. 30<br />

5.3 RESULTS .............................................................................................................. 30<br />

5.4 DISCUSSION .......................................................................................................... 32<br />

6) RESOURCE USE SURVEY ................................................................................... 33<br />

6.1 INTRODUCTION ...................................................................................................... 33<br />

6.2 METHODS ............................................................................................................. 33<br />

6.3 RESULTS .............................................................................................................. 33<br />

6.4 DISCUSSION .......................................................................................................... 37<br />

7) CONCLUSIONS AND RECOMMENDATIONS ...................................................... 38<br />

8) REFERENCES ....................................................................................................... 40


APPENDIX 1. HABITAT DETAILS FOR THE VEGETATION PLOTS IN THE EAST<br />

USAMBARAS ................................................................................................................... 41<br />

APPENDIX 2. LIST OF PLANTS FOUND IN THE MISALAI, SHAMBANGEDA AND<br />

KWATANGO VILLAGES’ LANDSCAPES. ...................................................................... 43<br />

APPENDIX 3. TRANSECT WALKS DATA...................................................................... 71<br />

APPENDIX 4. BIRD RINGING DATA. ............................................................................. 77<br />

APPENDIX 5. TIMED SPECIES COUNT DATA. ............................................................. 82<br />

APPENDIX 6. DEFINITION OF KEY LAND USE TYPES USED IN THE SURVEY ........ 91


Tanzania Forest Conservation Group<br />

The Tanzania Forest Conservation Group (TFCG) is a Tanzanian non-governmental organisation<br />

that has been promot<strong>in</strong>g <strong>the</strong> conservation <strong>of</strong> Tanzania‟s forests s<strong>in</strong>ce 1985. TFCG‟s mission is to<br />

conserve and restore <strong>the</strong> biodiversity <strong>of</strong> globally important forests <strong>in</strong> Tanzania for <strong>the</strong> benefit <strong>of</strong><br />

present and future generations. We achieve this through capacity build<strong>in</strong>g, advocacy, research,<br />

community development and protected area management, <strong>in</strong> ways that are susta<strong>in</strong>able and foster<br />

participation, cooperation and partnership.<br />

TFCG supports field based projects promot<strong>in</strong>g participatory forest management, environmental<br />

education, community development, advocacy and research <strong>in</strong> <strong>the</strong> Eastern Arc and Coastal<br />

Forests. TFCG also supports a community forest conservation network that facilitates l<strong>in</strong>kages<br />

between communities <strong>in</strong>volved <strong>in</strong> participatory forest management. To f<strong>in</strong>d out more about TFCG<br />

please visit our website www.tfcg.org<br />

TFCG is implement<strong>in</strong>g <strong>the</strong> Integrat<strong>in</strong>g Livelihoods and Multiple Biodiversity Values <strong>in</strong> Landscape<br />

Mosaics project <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

The World Agr<strong>of</strong>orestry Centre (ICRAF)<br />

ICRAF is an <strong>in</strong>ternational agr<strong>of</strong>orestry centre with <strong>the</strong> vision <strong>of</strong> transform<strong>in</strong>g rural livelihoods <strong>in</strong> <strong>the</strong><br />

develop<strong>in</strong>g world by <strong>in</strong>creas<strong>in</strong>g <strong>the</strong> use <strong>of</strong> trees <strong>in</strong> agricultural <strong>land</strong>scapes to improve food security,<br />

nutrition, <strong>in</strong>come, health, shelter, energy resources and environmental susta<strong>in</strong>ability.<br />

The mission <strong>of</strong> ICRAF is to generate science-based knowledge about <strong>the</strong> diverse roles that trees<br />

play <strong>in</strong> agricultural <strong>land</strong>scapes and to use its research to advance policies and practices that<br />

benefit <strong>the</strong> poor and <strong>the</strong> environment. ICRAF‟ s goal is to become a partner <strong>of</strong> choice for a range <strong>of</strong><br />

scientific and development <strong>in</strong>stitutions <strong>in</strong> <strong>the</strong>ir efforts to generate tree-based solutions to <strong>the</strong> global<br />

problems <strong>of</strong> rural poverty, hunger and environmental degradation.<br />

ICRAF and <strong>the</strong> Centre for International Forestry Research (CIFOR) jo<strong>in</strong>tly lead <strong>the</strong> Integrat<strong>in</strong>g<br />

Livelihoods and Multiple Biodiversity Values <strong>in</strong> Landscape Mosaics project that operates <strong>in</strong> five<br />

sites across <strong>the</strong> world.<br />

Contacts <strong>of</strong> TFCG:<br />

Tanzania Forest Conservation Group, PO Box 23410, Dar es Salaam, Tanzania<br />

E-mail: tfcg@tfcg.or.tz<br />

Tel.: +255 (0)22 2669007<br />

Website: www.tfcg.org


EXECUTIVE SUMMARY<br />

The East Usambara Mounta<strong>in</strong>s <strong>of</strong> north-east Tanzania are one <strong>of</strong> <strong>the</strong> 13 mounta<strong>in</strong> blocks that<br />

comprise <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s. The East Usambaras have high concentrations <strong>of</strong> endemic<br />

species <strong>in</strong>clud<strong>in</strong>g 7 endemic vertebrate species and 40 endemic tree species. However, most <strong>of</strong><br />

<strong>the</strong> biodiversity studies <strong>in</strong> <strong>the</strong> area have concentrated on <strong>the</strong> Central Government Catchment<br />

Forest Reserves and <strong>the</strong> Nature Reserves.<br />

This survey was conducted to assess <strong>the</strong> <strong>biological</strong> <strong>values</strong> <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> found <strong>in</strong><br />

three village <strong>land</strong>scapes <strong>in</strong> <strong>the</strong> East Usambaras by a team <strong>of</strong> researchers from <strong>the</strong> Tanzania<br />

Forest Conservation Group (TFCG). The survey was conducted as a part <strong>of</strong> <strong>the</strong> „Integrat<strong>in</strong>g<br />

Livelihoods and Multiple Biodiversity Values <strong>in</strong> Landscape Mosaics‟ project, a partnership project<br />

between CIFOR and ICRAF, implemented by TFCG <strong>in</strong> Tanzania.The project was funded by <strong>the</strong><br />

Swiss Agency for Development and Cooperation.<br />

The survey <strong>cover</strong>ed plants, mammals, birds and use <strong>of</strong> <strong>the</strong> tree and forest based resources <strong>in</strong> <strong>the</strong><br />

village <strong>land</strong>scapes by <strong>the</strong> communities. In addition, digital data was collected to validate previously<br />

produced <strong>land</strong> <strong>cover</strong> maps. Vegetation plots were used to assess plants with<strong>in</strong> <strong>the</strong> three<br />

<strong>land</strong>scapes. Mammals were ma<strong>in</strong>ly assessed by camera trapp<strong>in</strong>g method. A comb<strong>in</strong>ation <strong>of</strong><br />

methods was used to assess <strong>the</strong> birds: mist nett<strong>in</strong>g and timed-species count methods. Interviews<br />

were used to assess resource use by <strong>the</strong> local people.<br />

The survey team recorded 162 plant species from 67 families across <strong>the</strong> <strong>different</strong> <strong>land</strong> use <strong>types</strong> <strong>in</strong><br />

<strong>the</strong> three village <strong>land</strong>scapes. The team also recorded 10 mammal species. All <strong>the</strong> mammal species<br />

were recorded <strong>in</strong> <strong>the</strong> forests with<strong>in</strong> <strong>the</strong> village <strong>land</strong>s. In addition, 88 bird species were recorded <strong>in</strong><br />

<strong>the</strong> three village <strong>land</strong>scapes. The tree-based products that <strong>the</strong> local communities obta<strong>in</strong>ed from<br />

village <strong>land</strong>scapes <strong>in</strong>cluded local medic<strong>in</strong>es, timber, poles, fuelwoods, fruits and vegetables. A<br />

total <strong>of</strong> 56 species were mentioned to be used by <strong>the</strong> villagers. Most <strong>of</strong> <strong>the</strong>m were obta<strong>in</strong>ed from<br />

<strong>the</strong> agr<strong>of</strong>orest plots.<br />

The results <strong>of</strong> <strong>the</strong> survey <strong>in</strong>dicate that <strong>the</strong> village <strong>land</strong>scapes <strong>in</strong> <strong>the</strong> East Usambaras support<br />

considerable biodiversity resources. These resources are important for conservation and<br />

support<strong>in</strong>g <strong>the</strong> local livelihoods. Apart from <strong>the</strong> village forest reserves, <strong>the</strong> o<strong>the</strong>r <strong>land</strong> use <strong>types</strong> on<br />

village <strong>land</strong>s, such as agr<strong>of</strong>orests and fallows, support many valuable species that are also found<br />

<strong>in</strong> <strong>the</strong> forest reserves. None<strong>the</strong>less few <strong>of</strong> <strong>the</strong> East Usambara and Eastern Arc endemic species<br />

that are known from <strong>the</strong> East Usambaras were recorded dur<strong>in</strong>g <strong>the</strong> surveys. This highlights <strong>the</strong><br />

importance <strong>of</strong> adopt<strong>in</strong>g a <strong>land</strong>scape approach to conservation <strong>in</strong>clud<strong>in</strong>g both protected areas and<br />

<strong>land</strong> uses such as agr<strong>of</strong>orestry which provide habitat and corridors for some species.


Abbreviations and acronyms<br />

a.s.l above sea level<br />

CIFOR Centre for International Forestry Research<br />

DBH Diameter at Breast Height<br />

FBD Forestry and Beekeep<strong>in</strong>g Division<br />

FR Forest Reserve<br />

ICRAF The World Agr<strong>of</strong>orestry Centre<br />

IUCN International Union for Conservation <strong>of</strong> Nature<br />

MTSN Museo Trident<strong>in</strong>o di Scienze Naturali, Italy<br />

SDC Swiss Agency for Development and Cooperation<br />

TFCG Tanzania Forest Conservation Group<br />

TSC Timed Species Count<br />

VFR Village Forest Reserve<br />

1


Acknowledgements<br />

Fund<strong>in</strong>g<br />

The survey was funded by <strong>the</strong> Swiss Agency for Development and Cooperation through World Agr<strong>of</strong>orestry<br />

Centre (ICRAF) and CIFOR.<br />

Permission<br />

Permission to conduct this survey was k<strong>in</strong>dly provided by <strong>the</strong> Forestry and Beekeep<strong>in</strong>g Division <strong>of</strong> <strong>the</strong> M<strong>in</strong>istry<br />

<strong>of</strong> Natural Resources and Tourism and Muheza District Natural Resources Office.<br />

Survey team<br />

Team Leader: Nike Doggart<br />

Ecologist: Charles Leonard<br />

Botanist: Moses Mwangoka<br />

Ornithologist: Victor Mkongewa<br />

Field Asssistants: Francis and Benjam<strong>in</strong> (Shambangeda), Kanozo (Misalai), Gabriel Juma and Cosmas<br />

(Kwatango).<br />

Driver: Gerald Alphonce<br />

We are extremely grateful to <strong>the</strong> people <strong>of</strong> Misalai, Shambangeda and Kwatango for <strong>the</strong>ir co-operation <strong>in</strong><br />

carry<strong>in</strong>g out this survey. In particular, we would like to thank village leaders and all <strong>the</strong> villagers from Misalai,<br />

Shambangeda and Kwatango for shar<strong>in</strong>g <strong>the</strong>ir local knowledge and for giv<strong>in</strong>g us <strong>the</strong>ir support. We would also<br />

like to thank Mr. Emmanuel Lyimo, <strong>the</strong> site coord<strong>in</strong>ator <strong>of</strong> <strong>the</strong> project, for <strong>in</strong>valuable support to <strong>the</strong> work,<br />

<strong>in</strong>clud<strong>in</strong>g logistics. We are also grateful to Mr. Stal<strong>in</strong>e Kibet from East African Herbarium, National Museums <strong>of</strong><br />

Kenya for check<strong>in</strong>g <strong>the</strong> endemic and threatenes status <strong>of</strong> <strong>the</strong> plant species.<br />

Report writ<strong>in</strong>g and edit<strong>in</strong>g<br />

The report has been written by Charles Leonard and edited by Nike Doggart (TFCG) and He<strong>in</strong>i Vihemäki<br />

(ICRAF). We are also grateful to Salla Rantala from ICRAF and all those who provided advice and help when<br />

plann<strong>in</strong>g and conduct<strong>in</strong>g <strong>the</strong> survey. Ahsanteni sana!<br />

2


1) Introduction<br />

1.1 Background to <strong>the</strong> project<br />

This report documents <strong>the</strong> results <strong>of</strong> biodiversity surveys carried out <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s <strong>in</strong><br />

Tanzania as a part <strong>of</strong> <strong>the</strong> Integrat<strong>in</strong>g Livelihoods and Multiple Biodiversity Values <strong>in</strong> Landscape Mosaics<br />

project, also known as Landscape Mosaics project. It is a partnership project between CIFOR and ICRAF,<br />

f<strong>in</strong>anced by Swiss Agency for Development and Cooperation (SDC). In Tanzania, <strong>the</strong> project is implemented<br />

by <strong>the</strong> Tanzania Forest Conservation Group (TFCG) <strong>in</strong> partnership with ICRAF. The purpose <strong>of</strong> Landscape<br />

Mosaics project is to improve <strong>the</strong> livelihoods <strong>of</strong> <strong>the</strong> rural people and contribute to conservation <strong>of</strong> biodiversity<br />

<strong>values</strong> <strong>in</strong> <strong>the</strong> tropical <strong>land</strong>scape mosaics. The project is a multi-national project <strong>in</strong>volv<strong>in</strong>g five selected CIFOR-<br />

ICRAF field sites <strong>in</strong> Africa and Sou<strong>the</strong>ast Asia. The botanical survey, transect walk and resource use survey<br />

methods have been standardized across <strong>the</strong> sites.<br />

The biodiversity surveys aimed at assess<strong>in</strong>g <strong>the</strong> biodiversity <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> and <strong>the</strong> value <strong>of</strong> that<br />

biodiversity to <strong>the</strong> local people <strong>in</strong> <strong>the</strong> three <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango villages <strong>in</strong> <strong>the</strong><br />

East Usambara Mounta<strong>in</strong>s.<br />

1.2 Report structure<br />

The report is organized <strong>in</strong> seven sections. The report beg<strong>in</strong>s with an executive summary followed by an<br />

<strong>in</strong>troduction which conta<strong>in</strong>s <strong>the</strong> background <strong>of</strong> <strong>the</strong> project and an overview <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

The next five sections provide <strong>the</strong> results <strong>of</strong> <strong>the</strong> surveys on plants, birds, and mammals, <strong>the</strong> transect walks, as<br />

well as <strong>the</strong> results from <strong>the</strong> resource use <strong>in</strong>terviews. Each section <strong>in</strong>cludes <strong>in</strong>troduction, methodology, results<br />

and discussion. The f<strong>in</strong>al section <strong>in</strong>cludes <strong>the</strong> conclusions and recommendations <strong>of</strong> <strong>the</strong> study.<br />

1.3 An overview <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s<br />

The East Usambara Mounta<strong>in</strong>s <strong>of</strong> north-east Tanzania are one <strong>of</strong> <strong>the</strong> 13 mounta<strong>in</strong> blocks that comprise <strong>the</strong><br />

Eastern Arc Mounta<strong>in</strong>s. The Eastern Arc is a cha<strong>in</strong> <strong>of</strong> block-faulted, crystall<strong>in</strong>e mounta<strong>in</strong>s under <strong>the</strong> climatic<br />

<strong>in</strong>fluence <strong>of</strong> <strong>the</strong> Indian Ocean (Lovett, 1985). The East Usambara Mounta<strong>in</strong>s extend over an area <strong>of</strong> 1,082<br />

km 2 <strong>in</strong> Korogwe, Muheza and Mk<strong>in</strong>ga districts <strong>of</strong> Tanga region, between coord<strong>in</strong>ates 4°45´ and 5°20´ S and<br />

between 38°26´ and 38°48´ E. The mounta<strong>in</strong>s are located about 40 km away from <strong>the</strong> city <strong>of</strong> Tanga. To <strong>the</strong><br />

north west <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s lie <strong>the</strong> West Usambara Mounta<strong>in</strong>s.<br />

The ra<strong>in</strong>fall distribution is bi-modal, peak<strong>in</strong>g between March and May and between September and December.<br />

The dry seasons are from June to August and January to March. Ra<strong>in</strong>fall is greatest at higher altitudes and <strong>in</strong><br />

<strong>the</strong> south-eastern part <strong>of</strong> <strong>the</strong> mounta<strong>in</strong>s, <strong>in</strong>creas<strong>in</strong>g from 1,200 mm annually <strong>in</strong> <strong>the</strong> foothills to over 2,200 mm<br />

at higher altitudes. The west-fac<strong>in</strong>g slopes <strong>of</strong> <strong>the</strong> mounta<strong>in</strong>s are drier compared to <strong>the</strong> east-fac<strong>in</strong>g slopes due<br />

to climatic and topographical <strong>in</strong>teractions. Due to <strong>the</strong>ir age, isolation and <strong>the</strong>ir role as condensers <strong>of</strong> <strong>the</strong><br />

moisture from <strong>the</strong> Indian Ocean, <strong>the</strong> East Usambara Mounta<strong>in</strong>s support ancient and unique forests, rich <strong>in</strong><br />

endemic species (Hamilton, 1989).<br />

In <strong>the</strong> East Usambaras, <strong>the</strong>re are 32 forest reserves <strong>in</strong>clud<strong>in</strong>g two nature reserves, 10 Central Government<br />

Forest Reserves, eighteen Village Forest Reserves and two private forests with a total area <strong>of</strong> nearly 328 km 2 .<br />

The altitude <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s ranges from 130 m a.s.l <strong>in</strong> <strong>the</strong> low<strong>land</strong>s to 1,506 m a.s.l <strong>in</strong> <strong>the</strong><br />

high<strong>land</strong>s (Burgess et al., 2007).<br />

The East Usambara Mounta<strong>in</strong>s have <strong>the</strong> highest number <strong>of</strong> Eastern Arc endemic/near-endemic trees (40<br />

species) and about 35 Eastern Arc endemic and 42 near endemic vertebrates, exclud<strong>in</strong>g fish. In addition <strong>the</strong>re<br />

are 7 vertebrate species that are endemic to <strong>the</strong> East Usambara Mounta<strong>in</strong>s (Burgess et al., 2007). An<br />

3


additional 35 vertebrate species found <strong>in</strong> <strong>the</strong> East Usambaras are endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s and a<br />

fur<strong>the</strong>r 42 vertebrate species have ranges that also extend <strong>in</strong>to <strong>the</strong> coastal forests and nearby mounta<strong>in</strong><br />

ranges.<br />

The Eastern Arc Mounta<strong>in</strong> forests are <strong>the</strong> catchment area for <strong>the</strong> most <strong>of</strong> <strong>the</strong> ra<strong>in</strong>fall feed<strong>in</strong>g <strong>in</strong>to <strong>the</strong> large<br />

rivers <strong>in</strong> <strong>the</strong> eastern Tanzania. The East Usambara Mounta<strong>in</strong>s supply water to Sigi River, a vital source <strong>of</strong><br />

water for <strong>the</strong> local communities and <strong>the</strong> large city <strong>of</strong> Tanga.<br />

The proportion <strong>of</strong> recent forest loss <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s is quite high compared to o<strong>the</strong>r Eastern<br />

Arc Mounta<strong>in</strong>s <strong>of</strong> Tanzania. A recent study by Forestry and Beekeep<strong>in</strong>g Division (FBD, 2006) <strong>in</strong>dicates that <strong>the</strong><br />

forest loss between <strong>the</strong> 1970s and <strong>the</strong> early 21 st century was 12%. The same study estimates that <strong>the</strong><br />

wood<strong>land</strong>s <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s have decl<strong>in</strong>ed from 155 km 2 to almost 60 km 2 <strong>in</strong> <strong>the</strong> 2000s. A<br />

parallel study carried out by Ph.D. Jaclyn Hall with support from TFCG has shown that <strong>the</strong> rate <strong>of</strong> forest loss<br />

may be even considerably higher. Her data shows a loss <strong>of</strong> 33 % <strong>in</strong> <strong>the</strong> forest <strong>cover</strong> between 1975 and 2006.<br />

A number <strong>of</strong> factors have contributed to <strong>the</strong> loss <strong>of</strong> forest habitats <strong>in</strong> <strong>the</strong> East Usambara. These <strong>in</strong>clude forest<br />

fires, clearance <strong>of</strong> forested <strong>land</strong> for agriculture, commercial fuel wood collection, pitsaw<strong>in</strong>g, harvest<strong>in</strong>g for<br />

build<strong>in</strong>g materials, <strong>in</strong>clud<strong>in</strong>g poles and timber, and m<strong>in</strong><strong>in</strong>g.<br />

4


2) BOTANICAL SURVEYS<br />

2.1 Introduction<br />

The botanical surveys were conducted <strong>in</strong> <strong>the</strong> <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango villages.<br />

These areas have not been studied <strong>in</strong>-depth previously for <strong>the</strong>ir biodiversity value. Most surveys have<br />

concentrated on <strong>the</strong> Central Government Catchment Forest Reserves and <strong>the</strong> Nature Reserves, <strong>in</strong>clud<strong>in</strong>g<br />

<strong>in</strong>tensive biodiversity surveys carried out by Frontier-Tanzania <strong>in</strong> <strong>the</strong> 1990s. The aim <strong>of</strong> <strong>the</strong> botanical surveys<br />

we conducted was to assess <strong>the</strong> botanical <strong>values</strong> <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> terms <strong>of</strong> plant resources<br />

which are important for support<strong>in</strong>g people‟s livelihoods and species which are valuable for biodiversity<br />

conservation.<br />

2.2 Methods<br />

Twelve 10x200 m vegetation plots were established <strong>in</strong> <strong>the</strong> village <strong>land</strong>scapes <strong>of</strong> Misalai (four plots),<br />

Shambangeda (three plots) and Kwatango (five plots). With<strong>in</strong> <strong>the</strong>se plots, 1x40 m sub-plots were established<br />

for sapl<strong>in</strong>gs with dbh less than 10 cm, 5x40 m for trees with dbh greater than 10 cm but smaller than 30 cm<br />

and 10x200 m for trees with dbh greater than 30 cm. Species identification was done for each <strong>in</strong>dividual plant,<br />

<strong>in</strong>clud<strong>in</strong>g trees, sapl<strong>in</strong>gs, herbs, shrubs and climbers. Also <strong>the</strong> dbh and height <strong>of</strong> <strong>the</strong> plants were recorded.<br />

Specimens difficult to identify <strong>in</strong> <strong>the</strong> field were collected for fur<strong>the</strong>r identification <strong>in</strong> <strong>the</strong> herbarium.<br />

Out <strong>of</strong> <strong>the</strong> twelve vegetation plots established <strong>in</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> (see appendix 6), three were<br />

located with<strong>in</strong> <strong>the</strong> village forest reserves <strong>of</strong> Misalai, Shambangeda and Kwatango (one <strong>in</strong> each village forest<br />

reserve); three were with<strong>in</strong> agr<strong>of</strong>orestry sites and two with<strong>in</strong> fallow <strong>land</strong>s (table 1). In addition, one plot was<br />

established <strong>in</strong> a mosaic <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong>, <strong>in</strong>clud<strong>in</strong>g fallow <strong>land</strong>, agr<strong>of</strong>orest and monoculture, and<br />

ano<strong>the</strong>r one <strong>in</strong> a mosaic <strong>of</strong> monoculture and mixed farm<strong>in</strong>g. The rema<strong>in</strong><strong>in</strong>g two plots were established <strong>in</strong> an<br />

area <strong>of</strong> mixed farm<strong>in</strong>g and with<strong>in</strong> a teak plantation.<br />

Table 1. Frequency <strong>of</strong> vegetation plots <strong>in</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong>.<br />

Land Cover Type Number <strong>of</strong> plots<br />

Forest (with<strong>in</strong> village forest reserves) 3<br />

Agr<strong>of</strong>orestry 3<br />

Fallow <strong>land</strong> 2<br />

Mosaic <strong>of</strong> fallow <strong>land</strong>, agr<strong>of</strong>orestry, mixed farm<strong>in</strong>g and/or monoculture 2<br />

Mixed farm<strong>in</strong>g 1<br />

Teak plantation 1<br />

Habitat details were recorded at each vegetation plot. These <strong>in</strong>cluded details <strong>of</strong> topography, altitude, canopy<br />

height, shrub layer, ground layer, aspect, signs <strong>of</strong> past use and any o<strong>the</strong>r feature <strong>of</strong> <strong>in</strong>terest.<br />

In this study, a herb is def<strong>in</strong>ed as any seed-bear<strong>in</strong>g plant which does not have a woody stem. A shrub is<br />

def<strong>in</strong>ed as a woody plant with a dbh <strong>of</strong> less than 10 (exclud<strong>in</strong>g tree sapl<strong>in</strong>gs), which may be accompanied with<br />

several ma<strong>in</strong>stems aris<strong>in</strong>g at or near <strong>the</strong> ground.<br />

5


2.3 Results<br />

2.3.1 Number <strong>of</strong> <strong>in</strong>dividual plants recorded<br />

In total, 1,684 plants were found <strong>in</strong> <strong>the</strong> twelve vegetation plots established <strong>in</strong> <strong>the</strong> three village <strong>land</strong>scapes<br />

studied. Out <strong>of</strong> <strong>the</strong>se, 8% were trees above 30 cm dbh, 2% were trees rang<strong>in</strong>g dbh <strong>of</strong> 10-30cm, 35% were<br />

sapl<strong>in</strong>gs (30 cm<br />

dbh<br />

Number <strong>of</strong> trees<br />

10-30 cm<br />

dbh<br />


genus Albizia were also recorded <strong>in</strong> <strong>the</strong> forest reserves. The tree species <strong>in</strong>cluded Millettia usaramensis.<br />

Twelwe (12%) <strong>of</strong> <strong>the</strong> tree species were found <strong>in</strong> <strong>the</strong> mixed farm<strong>in</strong>g areas, <strong>of</strong> which one species; Dialium holtzii<br />

was also recorded <strong>in</strong> <strong>the</strong> forest reserves. In <strong>the</strong> <strong>land</strong> <strong>cover</strong> type consist<strong>in</strong>g <strong>of</strong> a mosaic <strong>of</strong> fallow <strong>land</strong>,<br />

agr<strong>of</strong>orest and monoculture, three (3%) tree species were recorded, <strong>of</strong> which none were recorded <strong>in</strong> <strong>the</strong> forest.<br />

Six (6%) <strong>of</strong> <strong>the</strong> tree species were recorded <strong>in</strong> <strong>the</strong> monoculture and mixed farm<strong>in</strong>g areas, <strong>of</strong> which none were<br />

recorded <strong>in</strong> <strong>the</strong> forest. In <strong>the</strong> teak plantation, twelwe (12%) tree species were recorded, <strong>of</strong> which none were<br />

recorded <strong>in</strong> <strong>the</strong> forest.<br />

Table 4. Tree species recorded <strong>in</strong> <strong>the</strong> <strong>land</strong>scapes <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

Vegetation/Land <strong>cover</strong> type Number <strong>of</strong> tree Number <strong>of</strong> tree species also<br />

species recorded recorded <strong>in</strong> <strong>the</strong> forests<br />

Village forest reserves 58 -<br />

Agr<strong>of</strong>orests 24 9<br />

Fallow <strong>land</strong>s 18 3<br />

Mixed farm<strong>in</strong>g plot 12 1<br />

Fallow <strong>land</strong>, agr<strong>of</strong>orest and<br />

3 0<br />

monoculture plot<br />

Monoculture and mixed farm<strong>in</strong>g plot 6 0<br />

Plantation 12 0<br />

Out <strong>of</strong> <strong>the</strong> shrub species, six (35%) species were recorded <strong>in</strong>side <strong>the</strong> village forest reserves (table 5). Seven<br />

(41%) species were recorded <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orest plots, <strong>of</strong> which two were also recorded <strong>in</strong> <strong>the</strong> village forest<br />

reserves. The list <strong>in</strong>cludes Whitfieldia elongata and Piper capense. Five (29%) <strong>of</strong> <strong>the</strong> shrub species were<br />

recorded <strong>in</strong> <strong>the</strong> monoculture and mixed farm<strong>in</strong>g plot. Six (35%) <strong>of</strong> <strong>the</strong> shrubs were recorded <strong>in</strong> <strong>the</strong> fallow <strong>land</strong>s,<br />

one (6%) <strong>of</strong> <strong>the</strong> shrubs were recorded <strong>in</strong> <strong>the</strong> mosaic <strong>of</strong> fallow <strong>land</strong>, agr<strong>of</strong>orest and monoculture plot and one<br />

(6%) <strong>of</strong> <strong>the</strong> shrub species was found <strong>in</strong> <strong>the</strong> mixed farm<strong>in</strong>g plot. Of <strong>the</strong>se species, none were recorded <strong>in</strong> <strong>the</strong><br />

village forest reserves.<br />

Table 5. Shrub species recorded <strong>in</strong> <strong>the</strong> <strong>land</strong>scapes <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

Vegetation/Land <strong>cover</strong> type Number <strong>of</strong> shrub species Number <strong>of</strong> shrub species<br />

recorded<br />

also recorded <strong>in</strong> <strong>the</strong> forests<br />

Village forest reserves 6 -<br />

Agr<strong>of</strong>orests 7 2<br />

Fallow <strong>land</strong>s 6 0<br />

Mixed farm<strong>in</strong>g plot 1 0<br />

Fallow <strong>land</strong>, agr<strong>of</strong>orest and<br />

monoculture plot<br />

1 0<br />

Monoculture and mixed<br />

farm<strong>in</strong>g plot<br />

5 0<br />

Plantation 1 0<br />

Out <strong>of</strong> <strong>the</strong> herb species, only two species (6%) were recorded <strong>in</strong> <strong>the</strong> village forest reserves. Twentytwo (71%)<br />

were recorded <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orest plots, out <strong>of</strong> which one was recorded also <strong>in</strong> <strong>the</strong> village forest reserves. Eleven<br />

herb species (35%) were recorded <strong>in</strong> <strong>the</strong> fallow <strong>land</strong>s, eight (26%) herb species <strong>in</strong> monoculture and mixed<br />

farm<strong>in</strong>g plot while four herb species (13%) were recorded <strong>in</strong> <strong>the</strong> mixed farm<strong>in</strong>g plot, as well as <strong>in</strong> <strong>the</strong> mosaic <strong>of</strong><br />

fallow <strong>land</strong>, agr<strong>of</strong>orest and monoculture. In <strong>the</strong> plantation, two herb species were recorded. None <strong>of</strong> <strong>the</strong> herb<br />

species recorded on <strong>the</strong> <strong>land</strong> uses o<strong>the</strong>r than agr<strong>of</strong>orests was also recorded <strong>in</strong> <strong>the</strong> village forests (table 6).<br />

7


Table 6. Herb species recorded <strong>in</strong> <strong>the</strong> <strong>land</strong>scapes <strong>of</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

Vegetation/Land <strong>cover</strong> type Number <strong>of</strong> herb species Number <strong>of</strong> herb species also<br />

recorded<br />

recorded <strong>in</strong> <strong>the</strong> forests<br />

Village forest reserves 2 -<br />

Agr<strong>of</strong>orests 22 1<br />

Fallow <strong>land</strong>s 11 0<br />

Mixed farm<strong>in</strong>g plot 4 0<br />

Fallow <strong>land</strong>, agr<strong>of</strong>orest and monoculture 4 0<br />

plot<br />

Monoculture and mixed farm<strong>in</strong>g plot 8 0<br />

Plantation 2 0<br />

In Misalai <strong>land</strong>scape, 70 plant species were recorded. The list <strong>in</strong>cludes valuable timber tree species Newtonia<br />

buchananii, found <strong>in</strong> <strong>the</strong> Misalai Village Forest Reserve (table 7).<br />

Table 7. List <strong>of</strong> species recorded <strong>in</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> Misalai village.<br />

Species<br />

Frequency per <strong>land</strong> <strong>cover</strong> type Uses<br />

Forest Agr<strong>of</strong>orest<br />

Fallow<br />

<strong>land</strong><br />

Adenia gummifera - - 1 -<br />

Agelaea pentagyna 1 - - -<br />

Albizia gummifera 6 - - -<br />

Alsodeiopsis schumannii - 1 - -<br />

Aoran<strong>the</strong> penduliflora - 1 - -<br />

8<br />

Monoculture &<br />

Mixed farm<strong>in</strong>g<br />

Artocarpus heterophyllus - - 1 -<br />

Asplenium sp - 37 - - Not used<br />

Bersama abyss<strong>in</strong>ica 2 - - -<br />

Bidens pilosa - - 1 4 Vegetable<br />

Boehmeria macrophylla - 19 -<br />

Bridelia micrantha - - 4 1<br />

Cedrela odorata - - - 1<br />

-<br />

Not used<br />

Build<strong>in</strong>g poles &<br />

fuelwood<br />

Chassalia parvifolia 9 1 - -<br />

C<strong>in</strong>namonum sp - 2 - 14 Spices & fuelwood<br />

Ro<strong>the</strong>ca myricoides - 1 - -<br />

Clidemia hirta - 3 5 - Not used<br />

C<strong>of</strong>fea Arabica - 1 - -<br />

Commel<strong>in</strong>a benghalensis - - 1 -<br />

Conyza sp - - 34 1 Not used<br />

Costus sp - 3 - -<br />

Culcasia sp - - - 2<br />

Dasylepis <strong>in</strong>tegra 1 - - -<br />

Desmodium repandum - 2 - -


Species<br />

Frequency per <strong>land</strong> <strong>cover</strong> type Uses<br />

Forest Agr<strong>of</strong>orest<br />

Dissotis rutondifolia - - 3<br />

Fallow<br />

<strong>land</strong><br />

Dracaena laxissima 5 - - -<br />

Ensete ventricosa - 1 - -<br />

Ficus thonn<strong>in</strong>gii 1 1 - -<br />

9<br />

Monoculture &<br />

Mixed farm<strong>in</strong>g<br />

Grevillea robusta - - 1 1<br />

Helichrysium<br />

odorattisimum - - 1 -<br />

Hibiscus sp - - - 6 Vegetables<br />

Impatiens sp - 3 - -<br />

Isoglosa lactea 2 1 - -<br />

Justicia sp - - 2 1<br />

Landolphia buchananii 2 - - -<br />

Lantana camara - - 8 36 Not used<br />

Lippia javanica - - - 18 Not used<br />

Macaranga<br />

kilimandscharica 4 - - -<br />

Maesa lanceolata 1 - - -<br />

Maesopsis em<strong>in</strong>ii - 4 - - Fuelwood & timber<br />

Manihot esculanta - - - 7<br />

Staple food &<br />

vegetable<br />

Milicia excelsa - - 2 -<br />

Myrianthus holstii 8 5 - - Fruits are edible<br />

Newtonia buchananii 5 - - -<br />

Oplismenus hirtellus - 2 - -<br />

Panicum sp - - 1 -<br />

Panicum trichocladum - - - 1<br />

Par<strong>in</strong>ari excelsa 4 - - -<br />

Paul<strong>in</strong>ia p<strong>in</strong>nata - - 1 -<br />

Pavetta abyss<strong>in</strong>ica var.<br />

usambarica 2 - - -<br />

Persea americana - 2 - 2<br />

Piper capense 9 3 - -<br />

Polycias fulva 1 - - -<br />

Pteris sp - - 17 29 Not used<br />

Quassia undulata 4 - - -<br />

Rawsonia reticulata - 2 - -<br />

Rothmannia urcelliformis - 2 - -<br />

Rubus sp - - 20 - Fruits are edible<br />

Shirakiopsis elliptica - 1 1 -


Species<br />

Frequency per <strong>land</strong> <strong>cover</strong> type Uses<br />

Forest Agr<strong>of</strong>orest<br />

Fallow<br />

<strong>land</strong><br />

10<br />

Monoculture &<br />

Mixed farm<strong>in</strong>g<br />

Solanum term<strong>in</strong>ale - 1 - -<br />

Sorghum sp - - 8 - Staple food<br />

Sor<strong>in</strong>deia<br />

Fruits are edible<br />

madagascariensis 144 6 - -<br />

Steganotaenia lauraceae - - - 2<br />

Strembosia scheffleri 1 - - -<br />

Saccharum <strong>of</strong>f<strong>in</strong>acirum - - - 3<br />

Tabernaemontana<br />

pachysiphon 2 - - -<br />

Triumfetta rhomboidea - - 2 11 Vegetable<br />

Vernonia lasiopus - - - 15 Not used<br />

Vernonia myriantha - - - 5<br />

Whiltifieldia sp 114 51 - -<br />

Xymalos monospora 3 2 - -<br />

Leaves used to cure<br />

fever<br />

Used as withies <strong>in</strong><br />

house construction<br />

A total <strong>of</strong> 54 plant species were recorded <strong>in</strong> <strong>the</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> Shambangeda village. The list<br />

<strong>in</strong>cludes Allanblackia stuhlmannii, one <strong>of</strong> <strong>the</strong> Eastern Arc near endemic tree species. The species was<br />

recorded <strong>in</strong>side <strong>the</strong> Shambangeda village forest reserve. O<strong>the</strong>r valuable timber tree species <strong>in</strong>cluded Newtonia<br />

buchananii and Milicia excelsa (table 8).<br />

Table 8. List <strong>of</strong> species recorded <strong>in</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> Shambangeda village.<br />

Species<br />

Frequency per <strong>land</strong> <strong>cover</strong> type Uses<br />

Forest Agr<strong>of</strong>orest<br />

Agelaea pentagyna 1 - -<br />

Albizia gummifera 1 - -<br />

Allanblackia stuhlmannii 14 - -<br />

Ananas comosus - 1 -<br />

Antiaris toxicaria 5 - -<br />

Artocarpus heterophyllus - - 2<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Monoculture (50%)<br />

Asplenium sp 1 - -<br />

Bidens pilosa - 14 5 Vegetable<br />

Bridelia micrantha - - 3<br />

Carvalhoa campanulata 2 - -<br />

Celtis gomphophylla 2 - -<br />

Cephalosphaera usambarensis 16 - -<br />

Chrysophyllum gorungosanum 1 - -<br />

Ro<strong>the</strong>ca myricoides 1 - -


Species<br />

Frequency per <strong>land</strong> <strong>cover</strong> type Uses<br />

Forest Agr<strong>of</strong>orest<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Monoculture (50%)<br />

Clidemia hirta - 1 -<br />

Conyza sp - 5 3 Not used<br />

Dracaena laxissima 4 - -<br />

Drypetes usambarica 1 - -<br />

Erythroxylum emarg<strong>in</strong>atum 1 - -<br />

Gal<strong>in</strong>iera saxifrage 1 - -<br />

Grevillia robusta - 3 1<br />

Ipomoea batatas - 1 -<br />

Landolphia buchananii 1 - -<br />

Lantana camara 4 -<br />

Leptaulus holstii 1 - -<br />

Macaranga kilimandscharica 3 - -<br />

Maesopsis em<strong>in</strong>ii 9 - -<br />

Manihot esculenta - 6 3<br />

Maytenus acum<strong>in</strong>ate 1 - -<br />

11<br />

Stems used as<br />

toothbrush.<br />

Staple food &<br />

vegetable<br />

Mesogyne <strong>in</strong>signis 8 - -<br />

Milicia excela - 5 - Timber<br />

Mimusops obtusifolia 1 - -<br />

Myrianthus holstii 2 - -<br />

Newtonia buchananii 2 - -<br />

Olyra latifolia 1 - -<br />

Par<strong>in</strong>ari excelsa 4 - -<br />

Pavetta abyss<strong>in</strong>ica var.<br />

usambarica 1 - -<br />

Polygala sp - 1 -<br />

Polyscias fulva 1 - -<br />

Pteris sp - 44 16<br />

Quassia undulata 3 - -<br />

R<strong>in</strong>orea angustifolia 70 - -<br />

R<strong>in</strong>orea ferrug<strong>in</strong>ea 2 - -<br />

Rothmannia urcelliformis 1 - -<br />

To make juice<br />

& local beer<br />

Saccharum <strong>of</strong>fic<strong>in</strong>arum - 39 37<br />

Synsepalum msolo 2 - - Staple food<br />

Sorghum sp - - 12<br />

-<br />

Sor<strong>in</strong>deia madagascariensis 12 -<br />

-


Species<br />

Frequency per <strong>land</strong> <strong>cover</strong> type Uses<br />

Forest Agr<strong>of</strong>orest<br />

Stachytapheta jamaicensis - 1 -<br />

Tabernaemontana pachysiphon 12 - -<br />

Tricalysia pallens 1 - -<br />

Trilepisium madagascariensis 1 - -<br />

Vepris simplicifolia 1 - -<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Monoculture (50%)<br />

Vernonia myriantha - 5 - -<br />

12<br />

Leaves used to<br />

cure fever<br />

In Kwatango, 81 plant species were recorded (table 9). The list <strong>in</strong>cluded an endemic tree species, <strong>in</strong>clud<strong>in</strong>g<br />

Cynometra engleri which was found only <strong>in</strong> <strong>the</strong> forest. The valuable timber tree species <strong>in</strong>cluded Milicia<br />

excelsa and Pterocarpus t<strong>in</strong>ctorius. Milicia excelsa was found <strong>in</strong> <strong>the</strong> fallow <strong>land</strong> and <strong>in</strong> <strong>the</strong> areas where mixed<br />

farm<strong>in</strong>g was practiced. Pterocarpus t<strong>in</strong>ctorius was found <strong>in</strong> <strong>the</strong> forest.<br />

Table 9. List <strong>of</strong> species recorded <strong>in</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> Kwatango village.<br />

Species Frequency per <strong>land</strong> <strong>cover</strong> type<br />

Forest Agr<strong>of</strong>orest Fallow<br />

<strong>land</strong><br />

Plantation Mixed<br />

farm<strong>in</strong>g<br />

Acalypha neptunica 20 - - - -<br />

Uses<br />

Acalypha volkensii - - 31 - - Not used<br />

Agelaea sp 1 - - - -<br />

Albizia adianthifolia 1 - - - -<br />

Albizia schimperiana - - 6 - - Timber<br />

Albizia sp - - - 4 1 Not used<br />

Alchornia hirtella 5 - - - -<br />

Allophylus pervillei - - - - 2<br />

Annona senegalensis - - - 1 -<br />

Annona sp - - 1 - -<br />

Antiaris toxicaria - - 4 - - Fuelwood<br />

Blighia unjugata - - 1 - -<br />

Bosqueiopsis gilletii 8 - - - -<br />

Bothriocl<strong>in</strong>e sp - 1 - - 8<br />

Bosqueopsis gilettii 1 - - - -<br />

Bridelia micrantha - 4 - - -<br />

Carpodiptera africana - - - 6 - Fuelwood<br />

Ceiba pertandra - - 2 - -<br />

Citrus s<strong>in</strong>ensis - 2 - - -<br />

Cola clavata 10 - - - -<br />

Commiphora Africana - - - 2 -<br />

Conyza sp - 38 - - 16 Not used


Species Frequency per <strong>land</strong> <strong>cover</strong> type<br />

Forest Agr<strong>of</strong>orest Fallow<br />

<strong>land</strong><br />

Plantation Mixed<br />

farm<strong>in</strong>g<br />

Cremaspora sp 2 - - - -<br />

Cussonia zimmermanii - - 3 2 -<br />

Cynometra engleri 4 - - - -<br />

Cynometra sp 13 - - - -<br />

De<strong>in</strong>bollia borbonica 2 1 7 - -<br />

Desmodium sp - - - 3 -<br />

Uses<br />

Dialium holtzii 22 - - - 6 Fuelwood<br />

& poles<br />

Dichapetalum sp - - - - 2<br />

Diospyros mespiliformis 10 2 - - -<br />

Dombeya kirkii - - - 7 - Fuelwood<br />

Dombeya mupangae - - - - 30 Not used<br />

Drypetes gerrard<strong>in</strong>oides 1 - - - -<br />

Elaeis gu<strong>in</strong>eensis - 1 - - -<br />

Emilia sp - 3 - - -<br />

Erythrococca fischeri - - 1 - -<br />

Ficus exasperata - 23 - - -<br />

Fluggea virosa - - 3 1 -<br />

Grewia forbesii - - - - 1<br />

Grewia similis - - 1 - -<br />

Harrissonia abyss<strong>in</strong>ica - - - 2 4 Not used<br />

Hostundia opposite - - 2 - -<br />

Justicia sp - - 3 - 1<br />

Landolphia buchananii 1 - - - -<br />

Lannea stuhlmannii - - 1 3 -<br />

Leptact<strong>in</strong>a platyphylla - 3 - - -<br />

Mangifera <strong>in</strong>dica - - 1 - -<br />

Manihot esculenta - 2 - - 1<br />

Manilkara sulcata 4 - - - -<br />

Markhamia sp 1 - - - -<br />

Milicia excelsa - - 7 - 3 Timber<br />

Millettia usaramensis 1 - 1 - -<br />

Musa sp - 5 - - - Fruits<br />

Ochna tomasiana 1 - - - -<br />

Panicum trichocladum - 1 1 1 1<br />

Paul<strong>in</strong>ia p<strong>in</strong>nata - - 1 - -<br />

Phyllanthus sp - 2 - - -<br />

Polysphaera lanceolata - - -<br />

13<br />

- 21 Fuelwood<br />

& poles


Species Frequency per <strong>land</strong> <strong>cover</strong> type<br />

Forest Agr<strong>of</strong>orest Fallow<br />

<strong>land</strong><br />

14<br />

Plantation Mixed<br />

farm<strong>in</strong>g<br />

Pouteria alnifolia 2 - - - -<br />

Premna sp - - - - 1<br />

Pseudobersama<br />

mossambicensis<br />

2 - - - -<br />

Pterocarpus t<strong>in</strong>ctorius 10 - - - -<br />

R<strong>in</strong>orea angustifolia 5 - -- - -<br />

Rothmannia engleriana 2 - -- - -<br />

Uses<br />

Rytigynia lichenoxenos - - - - 8 Fuelwood<br />

& poles<br />

Schizozygia c<strong>of</strong>faioides 9 - - - -<br />

Sclerochiton sp 2 - - - -<br />

Cassia abbreviata - - - 2<br />

Setaria megaphylla - - - 1 -<br />

Sonchus sp - 2 - - -<br />

Sterculia appendiculata - - - - 3<br />

Stereospermum kunthiomum - - - 2 -<br />

Strychnos mitis 1 - - -<br />

Tectona grandis - - - 2 -<br />

Thespesia garckeana - 1 - - -<br />

Trichilia emetica - - - 4 3 Timber &<br />

Fuelwood<br />

Trilepisium madagascariensis - 1 - - -<br />

Uvaria angolensis 1 - - - -<br />

Vernonia myriantha - - 2 - -<br />

Zea mays - 47 - - - Staple food<br />

2.3.3 Tree regeneration<br />

There were more sapl<strong>in</strong>gs <strong>in</strong> <strong>the</strong> forest than <strong>in</strong> o<strong>the</strong>r <strong>land</strong> <strong>cover</strong> <strong>types</strong> (table 2). In Misalai village forest, most <strong>of</strong><br />

<strong>the</strong> sapl<strong>in</strong>gs recorded were Sor<strong>in</strong>deia madagascariensis. In Shambangeda, R<strong>in</strong>orea angustifolia dom<strong>in</strong>ated. In<br />

Kwatango, Cynometra sp. and Diospyros mespiliformis were <strong>the</strong> most common ones.<br />

2.4 Discussion<br />

2.4.1 Valuable plant species for conservation<br />

One East Usambara endemic (Cynometra engleri) and three Eastern Arc endemic, and seven near endemic<br />

plant species were recorded. The Eastern Arc endemics <strong>in</strong>cluded Alsodeiopsis schumannii, Aoran<strong>the</strong><br />

penduliflora and Drypetes gerrard<strong>in</strong>oides.The Eastern Arc near-endemics <strong>in</strong>cluded Allanblackia stuhlmannii,<br />

Carvalhoa campanulata, Cephalosphaera usambarensis, Dasylepis <strong>in</strong>tegra, Dialium holtzii, Mesogyne <strong>in</strong>signis<br />

and Pouteria alnifolia. In addition, several species are endemic to <strong>the</strong> Zanzibar Inhambane Regional Mosaic<br />

Coastal forest (table 10).


Table 10. Checklist <strong>of</strong> all <strong>the</strong> plant species recorded <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

Genus Species Author<br />

East<br />

Usambara<br />

Endemic<br />

15<br />

Eastern<br />

Arc<br />

endemic<br />

Eastern<br />

Arc nearendemic<br />

Wide<br />

spread Exotic<br />

Acalypha volkensii Pax X NES<br />

Acalypha sp<br />

NA NA NA NA NA<br />

Adenia gummifera (Harv.) Harms X NES<br />

Agelaea pentagyna (Lam.) Baill X NES<br />

Agelaea sp NA NA NA NA NA<br />

Albizia adianthifolia (Schumach.) W.Wright X NES<br />

Albizia gummifera (J.F.Gmel.) C.A.Sm. X NES<br />

Albizia schimperiana Oliv. (var.amaniensis) X NES<br />

Albizia sp NA NA NA NA NA<br />

Alchornea hirtella Benth. X NES<br />

Allanblackia stuhlmannii Engl. X VU<br />

Allophylus pervillei Blume ZI NES<br />

Alsodeiopsis schumannii (Engl.) Engl. X VU<br />

Ananas comosus L. (Mer) X X NES<br />

Annona senegalensis Pers. X NES<br />

Annona sp<br />

Antiaris toxicaria<br />

NA NA NA NA NA<br />

Lesch. ssp. welwitschii var.<br />

usambarensis X NES<br />

Aoran<strong>the</strong> penduliflora (K.Schum) Somers X VU<br />

Artocarpus heterophyllus Lam X X NES<br />

Asplenium sp NA NA NA NA NA<br />

Thespesia garckeana (F. H<strong>of</strong>fm.) Excell & Hillcoat X NES<br />

Bersama abyss<strong>in</strong>ica Fresen. NES<br />

Bidens pilosa L. X NES<br />

Blighia unijugata Baker X NES<br />

Boehmeria macrophylla Hornem. X NES<br />

Bosqueiopsis gilletii De Wild. & T.Durand NES<br />

Bothriocl<strong>in</strong>e sp NA NA NA NA NA<br />

IUCN<br />

Threatened<br />

status


Genus Species Author<br />

East<br />

Usambara<br />

Endemic<br />

16<br />

Eastern<br />

Arc<br />

endemic<br />

Eastern<br />

Arc nearendemic<br />

Wide<br />

spread Exotic<br />

Bridelia micrantha (Hochst.) Baill. X NES<br />

Carvalhoa campanulata K. Schum. X NES<br />

Carpodiptera africana Mast. ZI NES<br />

Cassia abbreviata Oliv. NES<br />

Cedrela odorata L. X X VU<br />

Ceiba pentandra L. X X NES<br />

Celtis gomphophylla Baker NES<br />

Cephalosphaera usambarensis (Warb.) Warb. X VU<br />

Chassalia parvifolia K.Schum. X NES<br />

Chrysophyllum gorungosanum Engl. X NES<br />

C<strong>in</strong>namonum sp NA NA NA NA NA<br />

Citrus s<strong>in</strong>ensis (L.) Osbeck X X NES<br />

Clidemia hirta L. D. Don NES<br />

C<strong>of</strong>fea arabica L. X X<br />

Cola clavata Mast. ZI DD<br />

Commel<strong>in</strong>a benghalensis Wall. X<br />

Commiphora africana (A.Rich.) Engl. X NES<br />

Conyza sp NA NA NA NA NA<br />

Costus sp<br />

NA NA NA NA NA<br />

Cremaspora sp NA NA NA NA NA<br />

Culcasia sp NA NA NA NA NA<br />

Cussonia zimmermannii Harms ZI X LC<br />

Cynometra engleri Harms X VU<br />

Cynometra sp<br />

NA NA NA NA NA<br />

Dasylepis <strong>in</strong>tegra Warb. X VU<br />

De<strong>in</strong>bollia borbonica Scheffler X NES<br />

Desmodium repandum (Vahl) DC. X NES<br />

Desmodium sp<br />

NA NA NA NA NA<br />

Dialium holtzii Harms X VU<br />

IUCN<br />

Threatened<br />

status


Genus Species Author<br />

Dichapetalum sp<br />

East<br />

Usambara<br />

Endemic<br />

17<br />

Eastern<br />

Arc<br />

endemic<br />

Eastern<br />

Arc nearendemic<br />

Wide<br />

spread Exotic<br />

NA NA NA NA NA<br />

Diospyros mespiliformis Harms X NES<br />

Dissotis rotundifolia (Sm.) Triana X NES<br />

Dombeya kirkii Mast. X NES<br />

Dombeya mupangae K.Schum. X NES<br />

Dracaena laxissima Engl. X NES<br />

Drypetes usambarica (Pax) Hutch. ZI NES<br />

Drypetes gerrard<strong>in</strong>oides Radcl.-Sm X VU<br />

Elaeis gu<strong>in</strong>eensis Jacq. X NES<br />

Emilia sp<br />

NA NA NA NA NA<br />

Ensete ventricosum (Welw.) Cheesman X NES<br />

Erythrococca fischeri Pax NES<br />

Erythroxylum emarg<strong>in</strong>atum Thonn. X NES<br />

Ficus exasperata Vahl X NES<br />

Ficus thonn<strong>in</strong>gii Blume X NES<br />

Flueggea virosa (Willd.) Voigt X NES<br />

Gal<strong>in</strong>iera saxifraga (Hochst.) Bridson X NES<br />

Grevillea robusta A. Cunn. ex R.Br. X X NES<br />

Grewia forbesii Harv. ex Mast. X NES<br />

Grewia similis K.Schum. X NES<br />

Harrisonia abyss<strong>in</strong>ica Oliv. X NES<br />

Helichrysum odoratissimum (L.) Less. X NES<br />

Hibiscus sp<br />

NA NA NA NA NA<br />

Hoslundia opposita vahl X NES<br />

Impatiens sp<br />

NA NA NA NA NA<br />

Ipomoea batatas (L.) Lam. X X NES<br />

Isoglossa lactea L<strong>in</strong>dau ex Engl. X NES<br />

Justicia sp<br />

NA NA NA NA NA<br />

Landolphia buchananii (Hallier f.) Stapf X NES<br />

IUCN<br />

Threatened<br />

status


Genus Species Author<br />

East<br />

Usambara<br />

Endemic<br />

18<br />

Eastern<br />

Arc<br />

endemic<br />

Eastern<br />

Arc nearendemic<br />

Wide<br />

spread Exotic<br />

Lannea stuhlmannii (Engl.) Engl. X NES<br />

Lantana camara L. X X NES<br />

Leptact<strong>in</strong>a platyphylla (Hiern) Wernham X NES<br />

Leptaulus holstii (Engl.) Engl. X NES<br />

Lippia javanica (Burm.f.) Spreng. X NES<br />

Macaranga kilimandscharica Pax X NES<br />

Maesa lanceolata Forssk. X NES<br />

Maesopsis em<strong>in</strong>ii Engl. X NES<br />

Mangifera <strong>in</strong>dica L. X X DD<br />

Manihot esculenta L. X X NES<br />

Manilkara sulcata (Engl.) Dubard ZI* NES<br />

Markhamia sp<br />

NA NA NA NA NA<br />

Maytenus acum<strong>in</strong>ata (L.f.) Loes. X NES<br />

Mesogyne <strong>in</strong>signis Engl. X VU<br />

Milicia excelsa (Welw.) C.C.Berg X LR/NT<br />

Millettia usaramensis Taub. X NES<br />

Mimusops obtusifolia Lam. NES<br />

Musa sp<br />

NA NA NA NA NA<br />

Myrianthus holstii Engl.<br />

(Baker) G.C.C.Gilbert &<br />

X NES<br />

Newtonia buchananii Boutique X NES<br />

Ochna thomasiana Engl. & Gilg ex Engl. ZI NES<br />

Olyra latifolia L. X NES<br />

Oplismenus hirtellus (L.) P.Beauv. X NES<br />

Panicum trichocladum K.Schum. X NES<br />

Panicum sp<br />

NA NA NA NA NA<br />

Par<strong>in</strong>ari excelsa Sab<strong>in</strong>e X NES<br />

Paull<strong>in</strong>ia p<strong>in</strong>nata L.<br />

var. usambarica (Bremek)<br />

X NES<br />

Pavetta abyss<strong>in</strong>ica Bridson X VU?<br />

IUCN<br />

Threatened<br />

status


Genus Species Author<br />

East<br />

Usambara<br />

Endemic<br />

19<br />

Eastern<br />

Arc<br />

endemic<br />

Eastern<br />

Arc nearendemic<br />

Wide<br />

spread Exotic<br />

Persea americana Mill. X X NES<br />

Phyllanthus sp<br />

NA NA NA NA NA<br />

Piper capensis L.f. X NES<br />

Polygala sp<br />

NA NA NA NA NA<br />

Polyscias fulva (Hiern) Harms X NES<br />

Polysphaeria lanceolata Hiern X NES<br />

Pouteria alnifolia (Baker) Roberty X NES<br />

Premna sp<br />

NA NA NA NA NA<br />

Pseudobersama mossambicensis (Sim) Verdc. ZI X NES<br />

Pteris sp<br />

NA NA NA NA NA<br />

Pterocarpus t<strong>in</strong>ctorius Welw. X NES<br />

Quassia undulata (Guill. & Perr.) D.Dietr. X NES<br />

Rawsonia reticulata Gilg X LR/CD<br />

R<strong>in</strong>orea angustifolia (Thouars) Baill. NES<br />

R<strong>in</strong>orea ferrug<strong>in</strong>ea Engl.<br />

(Hochst.) D.A. Steane &<br />

ZI X NES<br />

Ro<strong>the</strong>ca myricoides Mabb. X<br />

Rothmannia urcelliformis (Hiern) Robyns X NES<br />

Rothmannia engleriana K.Schum<br />

Rubus sp<br />

Rytigynia lichenoxenos (K.Schum.) Robyns<br />

NA NA NA NA NA<br />

Saccharum <strong>of</strong>fic<strong>in</strong>arum L. X X NES<br />

Schizozygia c<strong>of</strong>faeoides Baill. NES<br />

Sclerochiton sp<br />

NA NA NA NA NA<br />

Setaria megaphylla (Steud.) T.Durand & Sch<strong>in</strong>z X NES<br />

Shirakiopsis elliptica (Hochst.) Kruijt NES<br />

Solanum term<strong>in</strong>ale Forssk. NES<br />

Sonchus sp<br />

Sorghum sp<br />

NA NA NA NA NA<br />

NA NA NA NA NA<br />

IUCN<br />

Threatened<br />

status


Genus Species Author<br />

East<br />

Usambara<br />

Endemic<br />

20<br />

Eastern<br />

Arc<br />

endemic<br />

Eastern<br />

Arc nearendemic<br />

Wide<br />

spread Exotic<br />

Sor<strong>in</strong>deia madagascariensis DC. X NES<br />

Stachytarpheta jamaicensis L. X NES<br />

Steganotaenia lauraceae ?<br />

Sterculia appendiculata K.Schum. ex Engl. ZI NES<br />

Stereospermum kunthianum Cham. X NES<br />

Strombosia scheffleri Engl. X NES<br />

Strychnos mitis S.Moore X NES<br />

Synsepalum msolo (Engl.) Penn<strong>in</strong>gton X NES<br />

Tabernaemontana pachysiphon Stapf X NES<br />

Tectona grandis L. X X NES<br />

Tricalysia pallens Hiern X NES<br />

Trichilia emetica Vahl X NES<br />

Trilepisium madagascariensis DC. X NES<br />

Triumfetta rhomboidea Jacq. X NES<br />

Uvaria angolensis Welw. ex Oliv X NES<br />

Vepris simplicifolia (Verdoorn) Mziray X NES<br />

Vernonia lasiopus O.H<strong>of</strong>fm. X NES<br />

Vernonia myriantha Hook.f. X NES<br />

Whitfieldia elongata (Beauv.) C.B.Cl. X NES<br />

Xymalos monospora (Harv.) Warb. X NES<br />

Zea mays L. X X NES<br />

Key to Table 10<br />

NES - No Evaluation status, NA - Not Applicable, VU – Vulnerable<br />

NT – Near threatened, DD – Data deficient, LR/NT – Lower risk/near threatened<br />

LR/CD – Lower risk/conservation dependant<br />

X - Status applies<br />

ZI - Endemic to Zanzibar Inhambane Regional Mosaic Coastal forest.<br />

ZI* - All collections are ZI except one from Mandera region <strong>of</strong> Kenyas<br />

IUCN<br />

Threatened<br />

status


In addition, fourteen <strong>of</strong> <strong>the</strong> tree species were found both <strong>in</strong> <strong>the</strong> village forest reserves and <strong>in</strong> o<strong>the</strong>r <strong>land</strong> use<br />

<strong>types</strong>, <strong>in</strong>cud<strong>in</strong>g agr<strong>of</strong>orests and fallow <strong>land</strong>s. These <strong>in</strong>cluded Millettia usaramensis, Dialium holtzii, Ficus<br />

thonn<strong>in</strong>gii, De<strong>in</strong>bollia borbonica, Diospyros mespiliformis and trees <strong>of</strong> <strong>the</strong> genus Albizia.<br />

The presence <strong>of</strong> East Usambara endemic and threatened plant species <strong>in</strong> <strong>the</strong> village forest reserves shows<br />

that <strong>the</strong>se forests play an important role <strong>in</strong> <strong>the</strong> conservation <strong>of</strong> <strong>the</strong> region‟s unique and threatened biodiversity.<br />

In addition, <strong>the</strong> trees <strong>in</strong> <strong>the</strong> Village Forest Reserves are used by <strong>the</strong> local people for various purposes, e.g. for<br />

timber, poles, local medic<strong>in</strong>es and fruits. This is discussed <strong>in</strong> detail <strong>in</strong> <strong>the</strong> Resource Use Survey <strong>in</strong> section six<br />

<strong>of</strong> this report.<br />

The study also recorded several valuable species <strong>in</strong> o<strong>the</strong>r <strong>land</strong> <strong>cover</strong> <strong>types</strong> than <strong>the</strong> village forest reserve. For<br />

<strong>in</strong>stance, some important timber tree species, <strong>in</strong>clud<strong>in</strong>g Milicia excelsa, were recorded <strong>in</strong> fallow <strong>land</strong>s,<br />

agr<strong>of</strong>orest plots and mixed farm<strong>in</strong>g areas. The trees are ei<strong>the</strong>r sold outside <strong>the</strong> village or utilized by <strong>the</strong><br />

villagers. Fur<strong>the</strong>rmore, <strong>the</strong> existence <strong>of</strong> <strong>the</strong>se tree species outside <strong>the</strong> forest reserves shows that also <strong>the</strong> nonreserved<br />

areas <strong>in</strong> <strong>the</strong> <strong>land</strong>scapes support valuable tree resources. Hence, while plann<strong>in</strong>g conservation<br />

strategies, <strong>the</strong> management <strong>of</strong> <strong>the</strong> tree resources outside <strong>the</strong> forest reserves should be addressed.<br />

2.4.2 O<strong>the</strong>r potential plant resources<br />

Food and cash crops were recorded <strong>in</strong> several <strong>land</strong> use <strong>types</strong> <strong>in</strong>clud<strong>in</strong>g agr<strong>of</strong>orest, mixed farm<strong>in</strong>g,<br />

monoculture and fallow <strong>land</strong>. Plant resources which were mentioned by <strong>the</strong> respondents to be used for food<br />

ranged from tubers and stems to fruits and seeds. The plants used for food <strong>in</strong>cluded cassava (Manihot<br />

esculenta), sugarcane (Saccharum <strong>of</strong>f<strong>in</strong>acirum), maize (Zea mays) and banana (Musa sp.). Cash crops<br />

cultivated <strong>in</strong>cluded cardamom (Elettaria cardamomum), c<strong>in</strong>namon (C<strong>in</strong>namonum sp.), clove and sugarcane.<br />

Most <strong>of</strong> <strong>the</strong> food and cash crops co-existed with o<strong>the</strong>r plants, <strong>in</strong>clud<strong>in</strong>g timber trees grow<strong>in</strong>g <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orests<br />

and fallow <strong>land</strong>s. The local people also used <strong>the</strong> tree resources <strong>in</strong> <strong>the</strong>se areas to get <strong>different</strong> products, such<br />

as firewood and timber.<br />

21


3) Transect walks<br />

3.1 Introduction<br />

The aim <strong>of</strong> conduct<strong>in</strong>g <strong>the</strong> transect walks was to provide data to validate <strong>the</strong> prelim<strong>in</strong>ary <strong>land</strong> <strong>cover</strong> maps<br />

produced from <strong>the</strong> <strong>in</strong>terpretation <strong>of</strong> <strong>the</strong> satellite images.<br />

3.2 Methods<br />

The first task was to identify and def<strong>in</strong>e <strong>the</strong> key <strong>land</strong> <strong>cover</strong> <strong>types</strong>. This was done <strong>in</strong> <strong>the</strong> field through rapid<br />

surveys and by us<strong>in</strong>g <strong>the</strong> project‟s draft <strong>land</strong> <strong>cover</strong> maps. The list <strong>of</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> identified is attached as<br />

Appendix 6.<br />

Secondly, <strong>the</strong> transects were located <strong>in</strong> <strong>the</strong> field by us<strong>in</strong>g <strong>the</strong> <strong>land</strong> <strong>cover</strong> maps and also through discussions<br />

with local <strong>in</strong>formants. This was to ensure that <strong>the</strong> transects wil <strong>cover</strong> an <strong>in</strong>clusive range <strong>of</strong> <strong>different</strong> <strong>land</strong> <strong>cover</strong><br />

<strong>types</strong>, such as village forests, plantations, tea estates, and agr<strong>of</strong>orests.<br />

At each site, straight l<strong>in</strong>e transects <strong>of</strong> one kilometer <strong>in</strong> length and ten meters wide were conducted (table 11).<br />

In total, eight hectares were <strong>cover</strong>ed by <strong>the</strong> transects. Only two transects were conducted <strong>in</strong> Shambangeda<br />

and Misalai <strong>land</strong>scapes because <strong>the</strong>se areas were not large enough to be surveyed by more than two<br />

transects. Four transects were conducted <strong>in</strong> Kwatango. After each 50 m, <strong>the</strong> <strong>land</strong> <strong>cover</strong> type was recorded<br />

with<strong>in</strong> <strong>the</strong> quadrat <strong>of</strong> 10 m around <strong>the</strong> po<strong>in</strong>t. At each <strong>of</strong> <strong>the</strong>se po<strong>in</strong>ts, where possible, a GPS read<strong>in</strong>g was<br />

taken. Photos were also taken at each po<strong>in</strong>t. Semi-structured <strong>in</strong>terviews were conducted with local <strong>in</strong>formants<br />

whilst walk<strong>in</strong>g <strong>the</strong> transects <strong>in</strong> order to understand <strong>the</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong>. In addition, local names for common<br />

plant species were recorded.<br />

Table 11. Number <strong>of</strong> transects conducted <strong>in</strong> <strong>the</strong> East Usambaras.<br />

Village <strong>land</strong>scape Number <strong>of</strong> transects<br />

Misalai 2<br />

Shambangeda 2<br />

Kwatango 4<br />

Total 8<br />

3.3 Results<br />

The <strong>land</strong> <strong>cover</strong> <strong>types</strong> recorded every after 50m section are presented <strong>in</strong> Appendix 3. In summary, each<br />

transect was characterized by hav<strong>in</strong>g at least three <strong>land</strong> use <strong>types</strong>, <strong>in</strong>clud<strong>in</strong>g agr<strong>of</strong>orests, fallow <strong>land</strong>s, tea<br />

fields, mixed farm<strong>in</strong>g sites and monoculture plots.<br />

3.4 Discussion<br />

Most <strong>of</strong> <strong>the</strong> fallow <strong>land</strong>s were recorded adjacent to agr<strong>of</strong>orest, mixed farm<strong>in</strong>g sites or monoculture plots<br />

suggest<strong>in</strong>g that <strong>the</strong> fallow <strong>land</strong>s were used for farm<strong>in</strong>g activities previously. The local <strong>in</strong>formants mentioned<br />

that most villagers <strong>in</strong> <strong>the</strong> area practice shift<strong>in</strong>g cultivation whereby a previously cultivated area is left fallow to<br />

return its fertility.<br />

22


4) Birds<br />

4.1 Introduction<br />

The East Usambara Mounta<strong>in</strong>s conta<strong>in</strong> six out <strong>of</strong> <strong>the</strong> 19 Eastern Arc endemic bird species and 13 out <strong>of</strong> 26<br />

near endemic species (Burgess et al., 2007). No s<strong>in</strong>gle-block endemic bird species have been reported <strong>in</strong> <strong>the</strong><br />

East Usambara Mounta<strong>in</strong>s (Baker and Baker, 2002).<br />

Birds <strong>of</strong> <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s are amongst <strong>the</strong> best studied taxa, as it is <strong>the</strong> case with o<strong>the</strong>r parts <strong>of</strong> <strong>the</strong><br />

world. The East Usambara Mounta<strong>in</strong>s are one <strong>of</strong> <strong>the</strong> most studied mounta<strong>in</strong> blocks <strong>in</strong> Tanzania. However,<br />

most <strong>of</strong> <strong>the</strong> studies were conf<strong>in</strong>ed to <strong>the</strong> sites which are managed by <strong>the</strong> central government authorities.<br />

The village <strong>land</strong>scapes visited dur<strong>in</strong>g this survey are part <strong>of</strong> <strong>the</strong> East Usambara Important Bird Area (Baker<br />

and Baker, 2002).<br />

4.2 Methods<br />

Two methods were used to assess <strong>the</strong> bird fauna <strong>of</strong> <strong>the</strong> three village <strong>land</strong>scapes: Mist nett<strong>in</strong>g and Timed<br />

Species Count (TSC). The surveys were conducted <strong>in</strong> <strong>the</strong> vic<strong>in</strong>ity <strong>of</strong> <strong>the</strong> vegetation plots.<br />

4.2.1 Mist nett<strong>in</strong>g<br />

Ten nets (five 12 m long and five 10 m long) were placed <strong>in</strong> a cont<strong>in</strong>uous l<strong>in</strong>e <strong>in</strong> each <strong>of</strong> <strong>the</strong> three sites for<br />

three days. The nets were opened early <strong>in</strong> <strong>the</strong> morn<strong>in</strong>g, checked frequently throughout <strong>the</strong> day and closed at<br />

dusk. Nett<strong>in</strong>g sites were at <strong>the</strong> vic<strong>in</strong>ity <strong>of</strong> <strong>the</strong> vegetation plots <strong>in</strong> <strong>the</strong> village forest reserves.<br />

Each captured bird was identified and morphometric measurements were taken <strong>in</strong>clud<strong>in</strong>g weight, bill, tarsus,<br />

w<strong>in</strong>g and tail. Where possible, sex and age were also recorded. Each capture was marked by a marker pen on<br />

<strong>the</strong> bill, as this made it easy to recognise recaptures thus avoid<strong>in</strong>g repeat<strong>in</strong>g records <strong>of</strong> <strong>the</strong> same bird. Two bird<br />

species were recaptured <strong>in</strong> Misalai: Olive sunbird and Little Greenbul (twice).<br />

4.2.2 Timed Species Count<br />

The field team walked quietly for a period <strong>of</strong> 60 m<strong>in</strong>utes at each vegetation plot <strong>in</strong> <strong>the</strong> morn<strong>in</strong>g, stopp<strong>in</strong>g<br />

frequently to identify and record all birds seen or heard call<strong>in</strong>g. Approximately an area <strong>of</strong> 1 km 2 was <strong>cover</strong>ed at<br />

each site. Notes were recorded <strong>in</strong> a notebook <strong>in</strong> order to compile a species list.<br />

4.3 Sampl<strong>in</strong>g <strong>in</strong>tensity<br />

The bird survey work was carried out by Victor Mkongewa, a field ornithologist; <strong>in</strong> three village <strong>land</strong>scapes <strong>of</strong><br />

Misalai, Shembangeda and Kwatango. Timed Species Counts were conducted <strong>in</strong> n<strong>in</strong>e vegetation plots while<br />

mist nett<strong>in</strong>g was conducted <strong>in</strong> <strong>the</strong> vic<strong>in</strong>ity <strong>of</strong> <strong>the</strong> three vegetation plots which were established <strong>in</strong> <strong>the</strong> forests.<br />

Timed species counts were conducted <strong>in</strong> <strong>the</strong> vegetation plots with <strong>the</strong> follow<strong>in</strong>g coord<strong>in</strong>ates <strong>in</strong> Misalai between<br />

15/02 – 16/02/2009: 0459964/9446401; 0459623/9444539 and 0459039/9443745 while mist nett<strong>in</strong>g was<br />

conducted at 0458902/9445582 between 3/11 – 5/11/2008 (Table 7). All sites were situated between 958 and<br />

1212 m a.s.l. For Shambangeda <strong>land</strong>scape, TSC was conducted between 17/02 – 18/02/2009 at<br />

0458710/9440288 and 0458786/9442508 while mist nett<strong>in</strong>g was conducted at 0459231/9440838 between<br />

25/10 – 28/10/2008, altitude ranged from 887 to 971 m a.s.l. In Kwatango village <strong>land</strong>scape, TSC was carried<br />

out at altitud<strong>in</strong>al variation <strong>of</strong> 178 to 233 m a.s.l. between 19/02 – 20/02/2009 at 0470734/9446282,<br />

0470745/9447458, 0471931/9443422 and 0471310/9445254 while mist nett<strong>in</strong>g was conducted between 30/10<br />

– 01/11/2008 at 0469746/9446451.<br />

23


A total <strong>of</strong> ten mist nets (five were 12 m long and <strong>the</strong> o<strong>the</strong>r five were 10 m long) were placed <strong>in</strong> <strong>the</strong> three<br />

<strong>land</strong>scapes for a total period <strong>of</strong> n<strong>in</strong>e days giv<strong>in</strong>g an average <strong>of</strong> 1320 net meter hours per full day <strong>of</strong> mist<br />

nett<strong>in</strong>g <strong>in</strong> each <strong>land</strong>scape (table 12). All <strong>of</strong> <strong>the</strong> mist nett<strong>in</strong>g was carried out with<strong>in</strong> <strong>the</strong> Village Forest Reserves<br />

whereas <strong>the</strong> timed species counts were made outside <strong>of</strong> <strong>the</strong> VFRs.<br />

Table 12. Summary for sampl<strong>in</strong>g <strong>in</strong>tensity for bird survey.<br />

Village<br />

<strong>land</strong>scape<br />

Total net meter<br />

hours<br />

Number <strong>of</strong> TSC<br />

days<br />

Altitud<strong>in</strong>al range (m<br />

a.s.l)<br />

24<br />

Period (mist nett<strong>in</strong>g<br />

and TSC respectively)<br />

Misalai 3960 2 958 – 1212 3/11 – 5/11/2008 and<br />

15/02 – 16/02/2009<br />

Shambangeda 3960 2 887 – 971 25/10 – 28/10/2008 and<br />

17/02 – 18/02/2009<br />

Kwatango 3960 2 178 – 233 30/10 – 01/11/2008 and<br />

19/02/ - 20/02/2009<br />

4.4 Results<br />

A total <strong>of</strong> 88 bird species were recorded through mist nett<strong>in</strong>g and Timed Species Counts <strong>in</strong> <strong>the</strong> three village<br />

<strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s. The species are listed<br />

<strong>in</strong> table 13.<br />

Table 13. Checklist <strong>of</strong> bird species from three village <strong>land</strong>scapes <strong>in</strong> <strong>the</strong> East Usambara Mounta<strong>in</strong>s.<br />

Species Common name Forest<br />

Dependency<br />

Range<br />

Threat Status<br />

(March 2009)<br />

Accipiter tachiro African goshawk F W LC 1<br />

Ale<strong>the</strong> fuelleborn White chested ale<strong>the</strong> FF W 1<br />

Andropadus masukuensis Shelley's greenbul FF EA N LC 1 1<br />

Andropadus striifaces Stripe-cheecked greenbul FF W 1<br />

Andropadus virens Little greenbul F W LC 1 1 1<br />

Anthreptes collaris Collared sunbird F W LC 1 1 1<br />

Anthreptes neglectus Uluguru violet backed sunbird F W LC 1<br />

Anthreptes pallidigaster Amani sunbird F EA N EN 1<br />

Anthreptes rubritorques Banded green sunbird FF EA E VU 1 1<br />

Apalis melanocephala Black headed apalis FF W LC 1<br />

Aplopelia larvata Lemon dove FF W LC 1<br />

Apus aff<strong>in</strong>is Little swift O W LC 1<br />

Artisornis moreaui Long-billed tailorbird<br />

F EA N<br />

CR 1<br />

Batis mixta Forest batis FF EA N LC 1<br />

Shambangeda<br />

Misalai<br />

Kwatango


Species Common name Forest<br />

Bias musicus<br />

25<br />

Dependency<br />

Range<br />

Threat Status<br />

(March 2009)<br />

Black- and -white shrikeflycatcher<br />

O W LC 1<br />

Bradypterus lopezi Evergreen forest warbler FF W LC 1 1<br />

Buteo oreophilus Mounta<strong>in</strong> buzzard F W LC 1 1<br />

Bycanistes brevis Silvery-cheeked hornbill FF W LC 1 1 1<br />

Bycanistes buc<strong>in</strong>ator Trumpeter hornbill F W LC 1 1<br />

Camaroptera brachyura Grey -backed camaroptera F W LC 1 1<br />

Centropus superciliosus White-browed coucal O W LC 1 1 1<br />

Cercococcyx montanus Barred Long-tailed cuckoo F W LC 1<br />

Ceuthmochares aereus Yellowbill F W LC 1<br />

Chrysococcyx cupreus African emerald cuckoo F W LC 1 1<br />

Chrysococcyx klaas Klaas's cuckoo F W LC 1 1<br />

Circaetus fasciolatus Sou<strong>the</strong>rn banded snake eagle F W NT 1<br />

Cisticola erythrops Red- faced cisticola O W LC 1 1 1<br />

Colius striatus Speckled mousebird O W LC 1 1 1<br />

Columba delegorguei Eastern bronze-naped pigeon F W LC 1 1<br />

Corac<strong>in</strong>a caesia Grey cuckoo-shrike FF W LC 1 1<br />

Cossypha heugl<strong>in</strong>i White-browed rob<strong>in</strong> chat O W LC 1<br />

Cryptospiza reichenovii Red faced crimsonw<strong>in</strong>g FF W LC 1<br />

Dicrurus adsimilis Fork tailed drongo F W LC 1 1<br />

Dicrurus ludwigii Square tailed drongo FF W LC 1 1 1<br />

Dryoscopus cubla Black-backed puffback F W LC 1 1<br />

Emberiza aff<strong>in</strong>is Cabanis bunt<strong>in</strong>g O W LC 1<br />

Estrilda astrild Common waxbill F W LC 1<br />

Euplectes capensis Yellow bishop O W LC 1<br />

Gypohierax angolensis Pulm-nut vulture O W LC 1<br />

Halcyon leucocephala Grey headed k<strong>in</strong>gfisher O W LC 1 1<br />

Hypargos margaritatus Peters' tw<strong>in</strong>spot F W LC 1<br />

Ispid<strong>in</strong>a lecontei African Pygmy K<strong>in</strong>gfisher O W LC 1<br />

Ispid<strong>in</strong>a picta O W LC 1<br />

Lamprotomis corruscus Black- bellied starl<strong>in</strong>g F W 1 1<br />

Laniarius aethiopicus Tropical boubou F W LC 1 1 1<br />

Lanius collaris Common fiscal O W LC 1 1<br />

Lonchura bicolor Black-and-white mank<strong>in</strong> O W LC 1 1<br />

Shambangeda<br />

Misalai<br />

Kwatango


Species Common name Forest<br />

26<br />

Dependency<br />

Range<br />

Threat Status<br />

(March 2009)<br />

Lophaetus occipitalis Long-crested eagle O W LC 1 1 1<br />

Malaconotus nigrifrons Black-fronted bush-shrike FF W 1<br />

Nectar<strong>in</strong>ia bifasciata Purple banded Sunbird O W LC 1 1 1<br />

Nectar<strong>in</strong>ia olivacea Olive Sunbird F W LC 1 1 1<br />

Neocossyphus rufus Red- tailed Ant-thrush FF W LC 1<br />

Nicator gularis Eastern Nicator F W LC 1 1<br />

Numida meleagris Helmeted Gu<strong>in</strong>eafowl F W LC 1<br />

Ploceus baglafect Baglafecht Weaver O W 1<br />

Ploceus bicolor Dark backed Weaver F W LC 1<br />

Ploceus cucullatus Black headed Weaver O W LC 1<br />

Ploceus subaureus African Golden Weaver O W LC 1<br />

Ploceus xanthops Golden Weaver O W LC 1<br />

Oriolus chlorocephlus Green- headed Oriole O W 1<br />

Phyllastrephus debilis T<strong>in</strong>y Greenbul FF W LC 1<br />

Phyllastrephus<br />

flavostriatus Yellow- streacked Greenbul FF W LC 1 1<br />

Platysteira peltata Black-throated Wattle-eye F W LC 1<br />

Ploceus bicolor Dark -backed Weaver F W LC 1<br />

Ploceus ocularis Spectacled Weaver O W LC 1<br />

Poeoptera kenricki Kenrick's Starl<strong>in</strong>g F EA N LC 1<br />

Pogonocichla stellata White-starred forest Rob<strong>in</strong> FF W LC 1<br />

Polyboroides typus African harrier Hawk F W LC 1 1<br />

Pr<strong>in</strong>ia subflava Tawny flanked Pr<strong>in</strong>ia O W LC 1 1 1<br />

Psalidoprocne holomelas Black saw-w<strong>in</strong>g O W<br />

Pycnonotus barbatus Common Bulbul O W LC 1 1 1<br />

Saxicola torquata Common Stonechat O W LC 1<br />

Ser<strong>in</strong>us cirr<strong>in</strong>elloides African Cirtil O W 1 1<br />

Ser<strong>in</strong>us mozambicus Yellow fronted Canary O W LC 1 1 1<br />

Stactolaema leucotis White-eared Barbet O W LC 1 1 1<br />

Stactolaema olivacea Green Barbet F EA N LC 1 1 1<br />

Stephanoaetus coronatus African crowned Eagle FF W LC 1 1 1<br />

Streptopelia semitorquata Red-eyed Dove F W LC 1 1<br />

Tauraco fischeri Fisher's turaco FF W NT 1 1 1<br />

Tchagra australis Brown-crowned Tchagra O W LC 1<br />

Shambangeda<br />

Misalai<br />

Kwatango


Species Common name Forest<br />

27<br />

Dependency<br />

Range<br />

Threat Status<br />

(March 2009)<br />

Tockus alboterm<strong>in</strong>atus Crowned Hornbill F W LC 1<br />

Treron calva African green Pigeon O W LC 1<br />

Trochocercus albonotatus White- tailed Crested flycatcher FF W LC 1<br />

Turdoides jard<strong>in</strong>eii Arrow-marked Babbler O W LC 1<br />

Turtur afer Blue-spotted wood Dove O W LC 1 1<br />

Turtur tympanistria Tambour<strong>in</strong>e Dove F W LC 1 1<br />

Vidua macroura P<strong>in</strong>- tailed Whydah O W LC 1 1<br />

Zosterops senegalensis Yellow White-eye F W LC 1 1 1<br />

Key to Table 13<br />

Forest dependency<br />

FF = strictly conf<strong>in</strong>ed to forest, F = ma<strong>in</strong>ly forest, but also found outside, O = non-forest species<br />

Range<br />

W = widespread, EAE= endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s, EAN= near endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s (also<br />

found <strong>in</strong> at least one o<strong>the</strong>r African ecoregion)<br />

Threatened status<br />

CR=Critically Endangered, EN=Endangered, NT=Near Threatened, LC=Least Concern<br />

In total, 256 observations were made through TSC compris<strong>in</strong>g 81 species. Similarly through mist nett<strong>in</strong>g, 122<br />

birds were r<strong>in</strong>ged from 17 species. Out <strong>of</strong> <strong>the</strong>se, 10 species were also sighted through TSC. Mist nett<strong>in</strong>g data<br />

from <strong>the</strong> three sites is attached as Appendix 4 and TSC data <strong>in</strong> Appendix 5.<br />

Olive sunbird, little Greenbul, Shelly‟s greenbul, yellow-streaked greenbul dom<strong>in</strong>ated <strong>the</strong> catch dur<strong>in</strong>g mist<br />

nett<strong>in</strong>g. This is a usual case for understorey birds.<br />

As <strong>the</strong> mist nett<strong>in</strong>g was conducted <strong>in</strong> October – February 2008 no birds with moult were observed. The<br />

breed<strong>in</strong>g season usually starts from August to February. Forest birds would be expected to moult towards <strong>the</strong><br />

end <strong>of</strong>, or immediately after <strong>the</strong> breed<strong>in</strong>g season. One olive sunbird was found with a brood patch <strong>in</strong><br />

Shambangeda and two African golden weavers and a spectacled weaver were recorded with breed<strong>in</strong>g<br />

plumage <strong>in</strong> Kwatango. Bird nests were also found: Sharpe‟s akalat, Little greenbul, African broadbill<br />

(Shambangeda), Purple-banded sunbird with two chicks and Forest batis (Kwatango).<br />

4.5 Discussion<br />

4.5.1 Species status and endemism<br />

The banded green sunbird Anthreptes rubritorques is <strong>the</strong> only Eastern Arc endemic bird species that was<br />

recorded dur<strong>in</strong>g <strong>the</strong> surveys. The bird was recorded <strong>in</strong> Misalai and Shambangeda village <strong>land</strong>scapes. Six bird<br />

species that are near-endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s were recorded dur<strong>in</strong>g <strong>the</strong> survey <strong>in</strong>clud<strong>in</strong>g<br />

Shambangeda<br />

Misalai<br />

Kwatango


Andropadus masukuensis, Anthreptes pallidigaster, Batis mixta, Poeptera kenricki, Stactolaema olivacea and<br />

Artisornis moreaui (table 14). The restricted range species recorded <strong>in</strong> <strong>the</strong> three <strong>land</strong>scapes <strong>of</strong> Misalai,<br />

Shambangeda and Kwatango have populations <strong>in</strong> o<strong>the</strong>r Eastern Arc Mounta<strong>in</strong>s and o<strong>the</strong>r sites <strong>in</strong>clud<strong>in</strong>g <strong>the</strong><br />

coastal forests, Sou<strong>the</strong>rn Rift and Kilimanjaro, Meru and Kenya Hig<strong>land</strong>s.<br />

Table 14. Eastern Arc endemic and near endemics found <strong>in</strong> <strong>the</strong> three village <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and<br />

Kwatango and <strong>the</strong>ir ranges.<br />

Species Common name Village <strong>land</strong>scape <strong>in</strong><br />

which was recorded<br />

Andropadus<br />

masukuensis<br />

Anthreptes<br />

pallidigaster<br />

Anthreptes<br />

rubritorques<br />

Artisornis moreaui<br />

Shelley's greenbul<br />

Shambangeda and<br />

Misalai<br />

Amani sunbird Shambangeda<br />

Banded green sunbird<br />

Long-billed tailorbird<br />

Shambangeda and<br />

Misalai<br />

Misalai<br />

Batis mixta Forest batis Shambangeda<br />

Poeoptera kenricki Kenrick's starl<strong>in</strong>g Kwatango<br />

Stactolaema<br />

olivacea<br />

Green barbet<br />

Misalai,<br />

Shambangeda and<br />

Kwatango<br />

28<br />

Range (Based on Burgess et<br />

al. 2007)<br />

South Pare, West Usambara,<br />

Nguu, Nguru, Uluguru, Ukaguru,<br />

Rubeho, Mahenge, Udzungwa<br />

and <strong>the</strong> Sou<strong>the</strong>rn Rift<br />

Udzungwa and coastal forests<br />

from Kenya to Mozambique<br />

West Usambara, Nguu, Nguru,<br />

Uluguru and Udzungwa<br />

East Usambara, Njesi Plateau <strong>in</strong><br />

Nor<strong>the</strong>rn Mozambique<br />

North Pare, South Pare, West<br />

Usambara, Nguu, Nguru,<br />

Udzungwa, Uluguru, Ukaguru,<br />

Rubeho, coastal forests from<br />

Kenya to Mozambique,<br />

Kilimanjaro, Meru and/or Kenya<br />

High<strong>land</strong>s<br />

South Pare, West Usambara,<br />

Nguu, Nguru, Uluguru, Rubeho,<br />

Udzungwa, Kilimanjaro, Meru<br />

and/or Kenya High<strong>land</strong>s and <strong>the</strong><br />

Sou<strong>the</strong>rn Rift<br />

West Usambara, Nguu, Nguru,<br />

Uluguru, Ukaguru, Rubeho,<br />

Udzungwa, coastal forests from<br />

Kenya to Mozambique and <strong>the</strong><br />

Sou<strong>the</strong>rn Rift<br />

In terms <strong>of</strong> degree <strong>of</strong> endemism, Shambangeda is particularly important as it has five out <strong>of</strong> seven <strong>of</strong> <strong>the</strong><br />

Eastern Arc endemic/near-endemic bird species recorded whilst Misalai and Kwatango have four and two<br />

Eastern Arc endemic/near-endemic bird species respectively.<br />

The long-billed tailor bird Artisornis moreaui, a critically endangered bird species (IUCN 2008) was only<br />

recorded <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orest plot <strong>in</strong> Misalai village <strong>land</strong>scape. The bird species was previously known to occur <strong>in</strong><br />

<strong>the</strong> Nilo Nature Reserve and <strong>the</strong> Amani Plateau <strong>in</strong> Tanzania and <strong>in</strong> <strong>the</strong> Njezi plateau <strong>of</strong> nor<strong>the</strong>rn Mozambique.<br />

O<strong>the</strong>r threatened bird species recorded <strong>in</strong>clude <strong>the</strong> Amani sunbird Anthreptes pallidigaster, banded green<br />

sunbird Anthreptes rubritorques, sou<strong>the</strong>rn banded snake eagle Circaetus fasciolatus and Fischer‟s turaco<br />

Tauraco fischeri (table 15).


Table 15. Threatened/near-threatened bird species recorded <strong>in</strong> <strong>the</strong> three village <strong>land</strong>scapes <strong>of</strong> <strong>the</strong> East Usambara<br />

Mounta<strong>in</strong>s.<br />

Species Common name Village <strong>land</strong>scape IUCN 2008 Threat<br />

Status<br />

Artisornis moreaui Long-billed tailorbird Misalai Critically Endangered<br />

Anthreptes pallidigaster Amani sunbird Shambangeda Endangered<br />

Anthreptes rubritorques Banded green sunbird Misalai and<br />

Shambangeda<br />

Vulnerable<br />

Circaetus fasciolatus Sou<strong>the</strong>rn banded snake eagle Shambangeda Near Threatened<br />

Tauraco fischeri Fischer‟s turaco Misalai,<br />

Shambangeda and<br />

Kwatango<br />

Near Threatened<br />

4.5.2 Species richness<br />

In terms <strong>of</strong> number <strong>of</strong> bird species, Misalai appears to be <strong>the</strong> richest with 57 species recorded, followed by<br />

Kwatango and lastly Shambangeda (table 16). Thus whilst species richness is lower <strong>in</strong> Shembangeda, <strong>the</strong><br />

number <strong>of</strong> restricted range species is highest.<br />

Table 16. Number <strong>of</strong> bird species recorded <strong>in</strong> each village <strong>land</strong>scape.<br />

Village <strong>land</strong>scape Number <strong>of</strong><br />

species<br />

Misalai 57<br />

Kwatango 51<br />

Shambangeda 42<br />

4.5.3 Habitat association<br />

Of <strong>the</strong> one Eastern Arc endemic and six Eastern Arc near-endemic bird species, all were found <strong>in</strong> agforest,<br />

fallow or plantation whilst only two, Batis mixta and Andropadus masukuensis were also found <strong>in</strong> <strong>the</strong> village<br />

forest reserves. Similarly all threatened bird species were found <strong>in</strong> agr<strong>of</strong>orest, fallow or plantation. To some<br />

extent this result reflects <strong>the</strong> difference <strong>in</strong> sampl<strong>in</strong>g <strong>in</strong>tensity whereby <strong>the</strong> village forest reserves were only<br />

sampled us<strong>in</strong>g mist nett<strong>in</strong>g whilst <strong>the</strong> <strong>land</strong> outside <strong>of</strong> <strong>the</strong> village forest reserves was only sampled us<strong>in</strong>g timed<br />

species counts. None<strong>the</strong>less, this does suggest that <strong>the</strong> agricultural mosaic is provid<strong>in</strong>g habitat for a significant<br />

number <strong>of</strong> threatened and restricted range bird species.<br />

29


5) Mammals<br />

5.1 Introduction<br />

The Mammal survey was conducted <strong>in</strong> <strong>the</strong> three <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango through<br />

camera trapp<strong>in</strong>g. Camera trapp<strong>in</strong>g method is normally used for survey<strong>in</strong>g cryptic animal species. Camera traps<br />

can be grouped accord<strong>in</strong>g to <strong>the</strong> type <strong>of</strong> sensor. In this study, we used heat <strong>in</strong> motion sensitive cameras.<br />

In Misalai, <strong>the</strong> camera traps were set <strong>in</strong> Misalai VFR while <strong>in</strong> Shambangeda, <strong>the</strong> camera traps were set <strong>in</strong> <strong>the</strong><br />

Derema forest. In Kwatango, <strong>the</strong> cameras were set <strong>in</strong> Kwemazaghati Village Forest Reserve. With<strong>in</strong><br />

Shambangeda it was not possible to f<strong>in</strong>d an appropriate place to put <strong>the</strong> camera traps, as such <strong>the</strong> traps were<br />

placed on Shembangeda village <strong>land</strong> with<strong>in</strong> <strong>the</strong> Derema forest.<br />

5.2 Methods<br />

The aim <strong>of</strong> camera trapp<strong>in</strong>g was to detect <strong>the</strong> presence <strong>of</strong> cryptic mammal species <strong>in</strong> <strong>the</strong> forested areas <strong>of</strong> <strong>the</strong><br />

three <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango.<br />

Camera traps (Deercam DC 300) were set to take photos 24- hours per day and were mounted with 36<br />

exposures Kodak 200 ISO films. Sites for camera-trapp<strong>in</strong>g were selected by <strong>in</strong>spect<strong>in</strong>g suitable <strong>land</strong>scape<br />

floors for wild animals‟ trails and o<strong>the</strong>r signs. The m<strong>in</strong>imum delay between consecutive photos was set at one<br />

m<strong>in</strong>ute. The camera traps were retrieved after a month. For each camera-trapped species, <strong>the</strong> number <strong>of</strong><br />

events (<strong>in</strong>dependent photos) was computed as <strong>the</strong> number <strong>of</strong> photos, not consider<strong>in</strong>g photos <strong>of</strong> <strong>the</strong> same<br />

species or <strong>in</strong>dividual taken with<strong>in</strong> <strong>the</strong> same hour.<br />

5.3 Results<br />

A total <strong>of</strong> ten species were camera-trapped out <strong>of</strong> 98 events (<strong>in</strong>dependent photos), see table 17 below for<br />

details.<br />

Table 17. Summary <strong>of</strong> camera-trapp<strong>in</strong>g effort and results obta<strong>in</strong>ed.<br />

Site Number <strong>of</strong> events Number <strong>of</strong> species<br />

Misalai 25 5<br />

Shambangeda 34 7<br />

Kwatango 39 9<br />

Total 98 21<br />

The list <strong>of</strong> <strong>the</strong> species trapped and number <strong>of</strong> events for each <strong>land</strong>scape are presented <strong>in</strong> tables 18-20 below.<br />

The comb<strong>in</strong>ed results are presented <strong>in</strong> table 21. Details <strong>of</strong> <strong>the</strong> trap sites are presented <strong>in</strong> <strong>the</strong> Appendices.<br />

In Misalai, three cameras were used out <strong>of</strong> which one did not work. The two operational cameras recorded 25<br />

events <strong>of</strong> five mammal species.<br />

Table 18. Camera-trapp<strong>in</strong>g results for Misalai.<br />

Species Number <strong>of</strong> events<br />

Black and rufous sengi (Rhychoncyon petersi) 2<br />

Squirrel (Paraxerus sp) 1<br />

Blotched genet (Genetta tigr<strong>in</strong>a) 2<br />

Suni (Neotragus moschatus) 4<br />

Giant-pouched rat (Cricetomys gambianus) 16<br />

Total 25<br />

30


In Shambangeda, four cameras were used out <strong>of</strong> which one did not work. The three cameras recorded 34<br />

events <strong>of</strong> five mammal species. The cameras also recorded two bird species: Hadada ibis and lemon dove.<br />

Table 19. Camera-trapp<strong>in</strong>g results for Shambangeda.<br />

Species Number <strong>of</strong> events<br />

Blotched genet (Genetta tigr<strong>in</strong>a) 8<br />

Suni (Neotragus moschatus) 3<br />

Giant-pouched rat (Cricetomys gambianus) 3<br />

Bushy-tailed mongoose (Bdeogale crassicauda) 13<br />

Banded mongoose (Mungos mungo) 1<br />

Total 28<br />

In Kwatango, seven cameras were used out <strong>of</strong> which one did not work. The rema<strong>in</strong><strong>in</strong>g six cameras recorded<br />

39 events <strong>of</strong> n<strong>in</strong>e species (table 20).<br />

Table 20. Camera-trapp<strong>in</strong>g results for Kwatango.<br />

Species Number <strong>of</strong> events<br />

Black and rufous sengi (Rhychoncyon petersi) 9<br />

Suni (Neotragus moschatus) 11<br />

Squirrel (Paraxerus sp) 1<br />

Giant-pouched rat (Cricetomys gambianus) 2<br />

Bushy-tailed mongoose (Bdeogale crassicauda) 2<br />

Banded mongoose (Mungos mungo) 1<br />

Baboon (Papio cynocephalus) 5<br />

Four-toed sengi (Petrodromus tetradactylus) 7<br />

African civet (Civettictis civetta) 1<br />

Total 39<br />

Table 21. Comb<strong>in</strong>ed camera-trapp<strong>in</strong>g results for <strong>the</strong> three <strong>land</strong>scapes and degree <strong>of</strong> endemism.<br />

Species Number <strong>of</strong> Endemism IUCN Threat<br />

events<br />

Status<br />

Black and rufous sengi (Rhychoncyon petersi) 11 N VU<br />

Suni (Neotragus moschatus) 18 W LR/cd<br />

Blotched genet (Genetta tigr<strong>in</strong>a) 10 W LC<br />

Squirrel (Paraxerus sp) 2 ? ?<br />

Giant-pouched rat (Cricetomys gambianus) 21 W LC<br />

Bushy-tailed mongoose (Bdeogale crassicauda) 15 W LC<br />

Banded mongoose (Mungos mungo) 2<br />

Baboon (Papio cynocephalus) 5 W LC<br />

Four-toed sengi (Petrodromus tetradactylus) 7 W LC<br />

African civet (Civettictis civetta) 1 W LC<br />

Total 92<br />

Key to Table 21<br />

Endemism<br />

N = near-endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s<br />

W = Widespread<br />

? = animal identified to genus only<br />

IUCN Threat Status<br />

VU = Vulnerable<br />

LR = Lower Risk<br />

LC = Least Concern<br />

31


5.4 Discussion<br />

5.4.1 Species richness and abundance<br />

An assumption is made that <strong>the</strong> frequency with which an animal species is photo-trapped reflects <strong>the</strong>ir<br />

abundance. With 10 species <strong>of</strong> mammals (Table 21), <strong>the</strong> species richness <strong>in</strong> <strong>the</strong> three forest <strong>land</strong>scapes <strong>of</strong><br />

Misalai, Shambangeda and Kwatango are relatively low when compared with o<strong>the</strong>r forests <strong>in</strong> <strong>the</strong> East<br />

Usambaras and <strong>in</strong> <strong>the</strong> Eastern Arc. By us<strong>in</strong>g <strong>the</strong> same method and comparable sampl<strong>in</strong>g efforts, TFCG/Trento<br />

Museum <strong>of</strong> Natural History, Italy surveys recorded 16 mammal species <strong>in</strong> <strong>the</strong> four forests <strong>of</strong> <strong>the</strong> Rubeho<br />

Mounta<strong>in</strong>s (Rovero 2008, unpbl.). In addition to <strong>the</strong> difference <strong>in</strong> <strong>the</strong> size <strong>of</strong> <strong>the</strong> forests; <strong>the</strong> variation is also<br />

likely to be due to hunt<strong>in</strong>g and habitat degradation that has reduced <strong>the</strong> mammal species diversity and<br />

abundance.<br />

The most common mammal species recorded were Suni and Giant pouched rat. No East Usambara or Eastern<br />

Arc endemic mammal species were recored from <strong>the</strong> <strong>land</strong>scapes surveyed. Most <strong>of</strong> <strong>the</strong> mammal species that<br />

were recorded are widespread.<br />

5.4.2 Threatened status<br />

Black and rufous sengi is <strong>the</strong> only species that was recorded dur<strong>in</strong>g <strong>the</strong> surveys which is categorized as be<strong>in</strong>g<br />

vulnerable accord<strong>in</strong>g to IUCN categories (IUCN, 2008). It is also near-endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s<br />

(Burgess et al., 2007).<br />

32


6) Resource use survey<br />

6.1 Introduction<br />

Most local communities <strong>in</strong> rural Tanzania depend on natural resources to support <strong>the</strong>ir livelihoods. In <strong>the</strong> East<br />

Usambara Mounta<strong>in</strong>s, <strong>the</strong> forest resources used most frequently by <strong>the</strong> local people <strong>in</strong>clude fuelwood, timber,<br />

poles, medic<strong>in</strong>al plants and food plants. The forests also provide valuable ecological services, such as<br />

reduc<strong>in</strong>g soil erosion.<br />

Resource use surveys were conducted by <strong>the</strong> survey team <strong>in</strong> <strong>the</strong> three study villages: Misalai, Shambangeda<br />

and Kwatango. The aim <strong>of</strong> <strong>the</strong> surveys was to ga<strong>the</strong>r <strong>in</strong>formation on uses <strong>of</strong> tree-based forest products by <strong>the</strong><br />

local communities <strong>in</strong> <strong>the</strong> <strong>land</strong>scape. Observations dur<strong>in</strong>g <strong>the</strong> field work and discussions with local people imply<br />

that most people <strong>in</strong> <strong>the</strong> study villages belong to Wasambaa tribe. Most <strong>of</strong> <strong>the</strong> villagers are subsistence farmers.<br />

The size <strong>of</strong> farm plots <strong>the</strong>y own ranges from two to four acres. Most people cultivate one or more cash crop,<br />

such as cardamom, c<strong>in</strong>namon, sugarcane and tea, and subsistence crops, such as maize, beans, bananas<br />

and cassava.<br />

6.2 Methods<br />

Interviews were conducted with selected groups <strong>of</strong> local villagers. The groups <strong>in</strong>cluded men and women. At <strong>the</strong><br />

start <strong>of</strong> <strong>the</strong> <strong>in</strong>terview, <strong>the</strong> researcher expla<strong>in</strong>ed <strong>the</strong> purpose <strong>of</strong> <strong>the</strong> <strong>in</strong>terview, which was to collect <strong>in</strong>formation on<br />

<strong>the</strong> resources that <strong>the</strong>y commonly use <strong>in</strong> <strong>the</strong> <strong>land</strong>scape. Then questions on various resource uses were asked,<br />

which were <strong>in</strong>tended to identify what <strong>the</strong> most important tree-based products and services that <strong>the</strong>y commonly<br />

use are.<br />

6.3 Results<br />

6.3.1 Tree-based products and services used by <strong>the</strong> local communities <strong>in</strong> Misalai<br />

In Misalai village, <strong>the</strong> respondents mentioned 46 wild species <strong>of</strong> plant that <strong>the</strong>y use with<strong>in</strong> <strong>the</strong>ir <strong>land</strong>scape<br />

<strong>in</strong>clud<strong>in</strong>g medic<strong>in</strong>al plants, fuelwood, timber, poles and wild fruits (table 22). Respondents also mentioned that<br />

<strong>the</strong>y obta<strong>in</strong> wild vegetables from <strong>the</strong> <strong>land</strong>scape. They expla<strong>in</strong>ed that <strong>the</strong>y obta<strong>in</strong> most <strong>of</strong> <strong>the</strong> medic<strong>in</strong>al plants<br />

from <strong>the</strong>ir agr<strong>of</strong>orestry plots, old fallows and nearby forests. In terms <strong>of</strong> <strong>the</strong> medic<strong>in</strong>al plants it is generally <strong>the</strong><br />

leaves, bark or roots <strong>of</strong> <strong>the</strong> plant that are used. The particular part <strong>of</strong> <strong>the</strong> plant can ei<strong>the</strong>r be boiled alone or<br />

mixed with some o<strong>the</strong>r <strong>in</strong>gredients to get <strong>the</strong> medic<strong>in</strong>e.<br />

Timber was obta<strong>in</strong>ed from <strong>the</strong> village <strong>land</strong>s, <strong>in</strong>clud<strong>in</strong>g agr<strong>of</strong>orest plots. Poles were commonly obta<strong>in</strong>ed from <strong>the</strong><br />

agr<strong>of</strong>orest areas. Fruits were collected from <strong>the</strong> agr<strong>of</strong>orest areas and <strong>the</strong> village forests. Wild vegetables were<br />

ma<strong>in</strong>ly obta<strong>in</strong>ed from <strong>the</strong> forests, <strong>in</strong>clud<strong>in</strong>g <strong>the</strong> village forest reserve and <strong>the</strong> agr<strong>of</strong>orest plots.<br />

Table 22. List <strong>of</strong> plant species used by local communities <strong>in</strong> <strong>the</strong> Misalai <strong>land</strong>scape.<br />

Local name Scientific /English name Land use type Use<br />

Mwaka Annickia kummeriae Agr<strong>of</strong>orest,old Leaves used to treat soles / ulcers;<br />

fallows<br />

roots used to treat gonorrhea<br />

Muuka Helichrysium sp VFR and<br />

Leaves used to treat human foot fungi<br />

Agr<strong>of</strong>orest<br />

and convulsions<br />

Mkwanga Tetrapleura tetraptera Agr<strong>of</strong>orest, old Leaves used as soap and roots used<br />

fallows and mixed<br />

farm<strong>in</strong>g plots<br />

to treat flu<br />

Mweyewana, Cajanus cajan (Pigeon peas) Agr<strong>of</strong>orest, old Roots used to treat convulsions<br />

33


Local name Scientific /English name Land use type Use<br />

Mbalazi fallows and mixed<br />

farm<strong>in</strong>g plont<br />

For treat<strong>in</strong>g ear problems<br />

Eza Solanecio sp VFR Leaves mixed with oyster nuts to treat<br />

<strong>in</strong>test<strong>in</strong>al worms<br />

Mzughwa Trilepisium madagascariensis Agr<strong>of</strong>orest Leaves used to treat malaria and fever<br />

Mhasha Vernonia myriantha Agr<strong>of</strong>orest Leaves used to cure fever<br />

Mzumbasha Ocimum suaveolens Agr<strong>of</strong>orest Leaves and roots used to treat chest<br />

diseases and <strong>in</strong>test<strong>in</strong>al worms<br />

Khozandogohyi Spectranthus sp Agr<strong>of</strong>orest Leaves were mentioned to treat<br />

Fwiza Unknown sp Agr<strong>of</strong>orest<br />

<strong>in</strong>test<strong>in</strong>al worms and convulsions<br />

Leaves and roots used to treat<br />

scabies<br />

Ulenge Unknown sp Agr<strong>of</strong>orest Leaves and roots used treats scabies<br />

Mkweme Telfairia pedata (oyster nut) VFR and<br />

The nuts are used to treat <strong>in</strong>test<strong>in</strong>al<br />

Agr<strong>of</strong>orest<br />

worms and oil is used by deliver<strong>in</strong>g<br />

mo<strong>the</strong>rs. Leaves are also used as<br />

vegetables.<br />

Longe Fern VFR For treat<strong>in</strong>g <strong>in</strong>test<strong>in</strong>al worms<br />

Mulungu Zanthoxylum usambarense Agr<strong>of</strong>orest Bark is used to treat <strong>in</strong>test<strong>in</strong>al worms<br />

and back aches<br />

Mtura Solanum <strong>in</strong>canum Agr<strong>of</strong>orest and old<br />

fallows<br />

For treat<strong>in</strong>g ear problems<br />

Mpapata Pandanus sp (P<strong>in</strong>eaple tree) Agr<strong>of</strong>orest For treat<strong>in</strong>g ear problems<br />

Mkulo Ocotea usambarensis (Camphor) Agr<strong>of</strong>orest Timber<br />

Mvule Milicia excels Agr<strong>of</strong>orest Timber<br />

Mnyasa Newtonia buchananii Agr<strong>of</strong>orest Timber<br />

Mkabela Grevillea robusta Agr<strong>of</strong>orest Timber<br />

Mkaratusi Eucalyptus sp Agr<strong>of</strong>orest Timber<br />

Mfimbo Beilschmiedia kweo Agr<strong>of</strong>orest Timber<br />

Mhesi Maesopsis em<strong>in</strong>ii Agr<strong>of</strong>orest Timber<br />

Mwiza Bridelia micrantha Agr<strong>of</strong>orest Timber<br />

Msambu Allanblackia stuhlmannii Agr<strong>of</strong>orest Timber<br />

Mshai Albizia gummifera Agr<strong>of</strong>orest Timber, Poles<br />

Mtambaa Cephalosphaera usambarensis Agr<strong>of</strong>orest Timber<br />

Sedelea Cederela odorata Agr<strong>of</strong>orest Timber<br />

Mlangalanga,<br />

Mparachichi<br />

Persea americana Agr<strong>of</strong>orest Timber, Poles<br />

Mfenesi Artocarpus heterophyllus Agr<strong>of</strong>orest Poles<br />

Mkungwira Sor<strong>in</strong>dea<br />

Madagascariensis<br />

VFR Fruits<br />

Msambia Synsepalum msolo VFR and mixed<br />

farm<strong>in</strong>g<br />

Fruits<br />

Samaka Afromomum sp VFR Fruits<br />

Mshaa Unknown sp. VFR and mixed<br />

farm<strong>in</strong>g<br />

Fruits<br />

Machuchu Unknown sp. Agr<strong>of</strong>orest Fruits<br />

Mstaferi Annona muricata Agr<strong>of</strong>orest Fruits<br />

Mnavu Solanum nigrum VFR and<br />

Agr<strong>of</strong>orest<br />

Vegetables<br />

Msangani Unknown sp. Agr<strong>of</strong>orest Vegetables<br />

Ndelema Basella alba Agr<strong>of</strong>orest Vegetables<br />

34


Local name Scientific /English name Land use type Use<br />

Mchunga Sonchos sp Agr<strong>of</strong>orest Vegetables<br />

Mbwembwe Bidens pilosa Agr<strong>of</strong>orest Vegetables<br />

6.3.2 Most important <strong>in</strong>come generat<strong>in</strong>g tree-based products and services <strong>in</strong> Misalai<br />

Accord<strong>in</strong>g to <strong>the</strong> respondents, seven non-timber forest products that provide <strong>the</strong>m with <strong>the</strong> most <strong>in</strong>come<br />

<strong>in</strong>cluded Allanblackia, c<strong>in</strong>namon, cardamom, cloves, c<strong>of</strong>fee, oyster nuts and taro tubers. The plant products<br />

that earn <strong>the</strong> greatest <strong>in</strong>comes are listed <strong>in</strong> table 23. Respondents also mentioned bananas, beans and sugar<br />

cane as be<strong>in</strong>g important traded products.<br />

Table 23. List <strong>of</strong> non-timber and timber forest products that br<strong>in</strong>g <strong>the</strong> most <strong>in</strong>come <strong>in</strong> Misalai Landscape and <strong>the</strong>ir prices.<br />

Local name Scientific/English name Land use type Price (Tshs)<br />

Masambu Seeds <strong>of</strong> Allanblackia stuhlmannii VFR and Agr<strong>of</strong>orest 250 per kg <strong>of</strong> seeds<br />

Dalas<strong>in</strong>i C<strong>in</strong>namomum zeylanicum Agr<strong>of</strong>orest<br />

Iliki Cardamon Monoculture and Agr<strong>of</strong>orest 3,000 per kg<br />

Karafuu Cloves Agr<strong>of</strong>orest 4,000 per kg<br />

Kahawa C<strong>of</strong>fea arabica Agr<strong>of</strong>orest 1,500 per kg<br />

Makweme Oyster nuts (Telfairia pedata) VFR and Agr<strong>of</strong>orest 5,000 per basket<br />

Mbao Timber Forest and Agr<strong>of</strong>orest 1,500 – 5,000 per piece<br />

depend<strong>in</strong>g on size<br />

Magimbi Taro tubers (Colocasia sp) Agr<strong>of</strong>orest 11,000 – 13,000 per 50 kg<br />

bag<br />

6.3.3 Tree-based products and services used by <strong>the</strong> local communities <strong>in</strong> Shambangeda<br />

In Shembangeda, <strong>the</strong> villagers stated that wild plant products that <strong>the</strong>y harvest with<strong>in</strong> <strong>the</strong>ir village <strong>land</strong>scape<br />

<strong>in</strong>clude: fuelwood, local medic<strong>in</strong>es, mushrooms, Allanblackia fruits, timber and poles (table 24). Accord<strong>in</strong>g to<br />

he respondents, <strong>the</strong>y ma<strong>in</strong>ly collected timber and poles from <strong>the</strong> agr<strong>of</strong>orest areas after seek<strong>in</strong>g a permit from<br />

<strong>the</strong> village government. Allanblackia, local medic<strong>in</strong>es, mushrooms and fuelwood are obta<strong>in</strong>ed with<strong>in</strong> <strong>the</strong> forests<br />

<strong>in</strong> <strong>the</strong>ir areas <strong>in</strong>clud<strong>in</strong>g <strong>the</strong> VFR as well as <strong>the</strong> agr<strong>of</strong>orest plots.<br />

Table 24. List <strong>of</strong> plant species used by local communities <strong>in</strong> <strong>the</strong> Shambangeda <strong>land</strong>scape.<br />

Local name Scient/Engl name Land use type Use<br />

Muuka Helichrysium sp Forest and agr<strong>of</strong>orest Leaves are used to treat <strong>in</strong>test<strong>in</strong>al worms<br />

Mkwanga Tetrapleura tetraptera Forest and agr<strong>of</strong>oret Leaves are used to treat Kambaku”<br />

Mwaka Annickia kummeriae Forest and agr<strong>of</strong>orest Leaves are used to treat sores/ulcers<br />

Mzughwa Trilepisium madascariensis Forest and agr<strong>of</strong>orest For treat<strong>in</strong>g malaria<br />

Mhesi Maesopsis em<strong>in</strong>ii Forest and agr<strong>of</strong>orest Fuelwood<br />

The respondents <strong>in</strong> Shambangeda village mentioned medic<strong>in</strong>al plants and fuelwood to be <strong>the</strong> most important<br />

tree based products that <strong>the</strong>y are obta<strong>in</strong><strong>in</strong>g with<strong>in</strong> <strong>the</strong>ir <strong>land</strong>scape. The third one was water <strong>in</strong>clud<strong>in</strong>g ra<strong>in</strong>s<br />

which <strong>the</strong>y l<strong>in</strong>ked with <strong>the</strong>ir efforts to conserve <strong>the</strong>ir <strong>land</strong>scapes well, <strong>in</strong>clud<strong>in</strong>g <strong>the</strong> forest. Allanblackia fruits,<br />

mushroom and timber were also mentioned to be important.<br />

6.3.4 Most important <strong>in</strong>come generat<strong>in</strong>g tree-based products and services <strong>in</strong> Shambangeda<br />

Timber, fuelwood, Allanblackia fruits, cardamon, c<strong>in</strong>namon, cloves, sugar cane and black pepper were<br />

mentioned as <strong>the</strong> tree–based products which are most traded <strong>in</strong> <strong>the</strong> area. Most <strong>of</strong> <strong>the</strong> products are sold<br />

35


outside <strong>the</strong> village, although timber is mostly traded with<strong>in</strong> <strong>the</strong> village. Most <strong>of</strong> <strong>the</strong> fuelwood is sold to tea<br />

factories whilst most <strong>of</strong> <strong>the</strong> sugarcane is sold to Dar es Salaam and Tanga cities. Timber was obta<strong>in</strong>ed from<br />

<strong>the</strong> agr<strong>of</strong>orest areas, for which a permit had to be applied first from <strong>the</strong> village government. Mhesi (Maesopsis<br />

em<strong>in</strong>ii) was among <strong>the</strong> most preferred tree species for fuelwood.<br />

Table 25. List <strong>of</strong> plant species that br<strong>in</strong>g <strong>the</strong> most <strong>in</strong>come <strong>in</strong> Shembangeda <strong>land</strong>scape and <strong>the</strong>ir prices.<br />

Local name Scient/English name Land use type Price(Tshs)<br />

Mbao Timber Agr<strong>of</strong>orest 2,500-3000 per piece<br />

Kuni Fuelwood VRF and Agr<strong>of</strong>orest 1,500 per 3ft<br />

Masambu Seeds <strong>of</strong> Allanblackia stuhlmannii VFR and Agr<strong>of</strong>orest 200 per kg<br />

Miwa Sugarcane Monoculture sites 80-100 per piece<br />

Iliki Cardamon Agr<strong>of</strong>orest and<br />

monoculture sites<br />

2,500-3000 per kg<br />

Mdalas<strong>in</strong>i C<strong>in</strong>namomum zeylanicum Forest and Agr<strong>of</strong>orest 700 per kg<br />

Karafuu Clove Agr<strong>of</strong>orest<br />

Pilipili manga Black pepper Agr<strong>of</strong>orest<br />

6.3.5 Tree-based products and services used by <strong>the</strong> local communities <strong>in</strong> Kwatango<br />

In Kwatango village, respondents mentioned timber, poles, fuelwood, fruits and local medic<strong>in</strong>es as tree –<br />

based products which <strong>the</strong>y obta<strong>in</strong> <strong>in</strong> <strong>the</strong>ir areas (table 26). They mentioned to get timber and poles from <strong>the</strong><br />

forests with<strong>in</strong> <strong>the</strong>ir areas as well as <strong>in</strong> o<strong>the</strong>r areas such as old fallow <strong>land</strong>s and agr<strong>of</strong>orests. The respondents<br />

mentioned to obta<strong>in</strong> medic<strong>in</strong>al plants from <strong>the</strong> forests and also <strong>in</strong> areas with<strong>in</strong> <strong>the</strong> village <strong>land</strong> <strong>in</strong>clud<strong>in</strong>g<br />

agr<strong>of</strong>orest plots and valleys. Mjavikazi was <strong>the</strong> only plant mentioned as be<strong>in</strong>g found only <strong>in</strong> forests around <strong>the</strong><br />

area <strong>in</strong>clud<strong>in</strong>g <strong>the</strong> Village Forest Reserve. The tree was mentioned to treat men‟s sexual hormone problems.<br />

36


Table 26. List plant species used by local communities <strong>in</strong> <strong>the</strong> Kwatango <strong>land</strong>scape.<br />

Local name Scientific/Englis name Land use type Use<br />

Mbambak<strong>of</strong>i Afzelia quanzensis Forest and Agr<strong>of</strong>orest Timber<br />

Mkenge Albizia versicolor Forest and Agr<strong>of</strong>orest Timber and local medic<strong>in</strong>es – treat<br />

chest problems and “kambaku”<br />

Mn<strong>in</strong>ga Pterocarpus t<strong>in</strong>ctorius Forest and Agr<strong>of</strong>orest Timber and Poles<br />

Mvule Milicia excelsa Forest and Agr<strong>of</strong>orest Timber<br />

Mitiki Tectona grandis, teak Plantation and Agr<strong>of</strong>orest Timber and Poles<br />

Mgude Sterculia appendiculata Forest and Agr<strong>of</strong>orest Timber<br />

Mpopote Unknown sp. Forest and Agr<strong>of</strong>orest Timber<br />

Khozandoghoi Spectranthus sp Old fallow <strong>land</strong>s Roots used to treat <strong>in</strong>test<strong>in</strong>al worms<br />

Mzughwa Trilepisium<br />

Agr<strong>of</strong>orest For treat<strong>in</strong>g malaria<br />

madagascariensis<br />

Mtura Solanum <strong>in</strong>canum Agr<strong>of</strong>orest For treat<strong>in</strong>g stomach problems<br />

Mhasha Vernonia myriantha Agr<strong>of</strong>orest For treat<strong>in</strong>g chest problems.<br />

Mwengee Unknown sp. ? For treat<strong>in</strong>g sores/ulcers<br />

Mjavikazi Unknown sp. Forest reserve Roots used to treat men‟s sexual<br />

hormonal problems<br />

Mfleta and Albizia an<strong>the</strong>lm<strong>in</strong>tica Agr<strong>of</strong>orest For treat<strong>in</strong>g body tiredness<br />

Msaji Senna siamea Agr<strong>of</strong>orest For treat<strong>in</strong>g body tiredness<br />

Mwaroba<strong>in</strong>i Azadirachta <strong>in</strong>dica Agr<strong>of</strong>orest For treat<strong>in</strong>g malaria and pesticide<br />

6.3.6 Most impotant <strong>in</strong>come generat<strong>in</strong>g tree-based products and services <strong>in</strong> Kwatango<br />

Timber, poles and fuelwood were <strong>the</strong> most frequently traded products with<strong>in</strong> <strong>the</strong> village and outside (table 26).<br />

Accord<strong>in</strong>g to <strong>the</strong> respondents, mitiki (Tectona grandis), mkenge (Albizia vescolar), mvule (Milicia excelsa),<br />

mn<strong>in</strong>gamaji (Pterocarpus t<strong>in</strong>ctorius), mbambak<strong>of</strong>i (Afzelia quanzensis), mpopote and mgule (Sterculia<br />

appendiculata) were among <strong>the</strong> species traded <strong>in</strong> <strong>the</strong>ir area.<br />

The price for timber was reported to vary depend<strong>in</strong>g on <strong>the</strong> type and size <strong>of</strong> <strong>the</strong> timber. Generally, <strong>the</strong>y stated<br />

<strong>the</strong> price to range from Tshs 2,000 to Tshs 3,000 per 10 ft piece. For poles, <strong>the</strong> price ranged from Tshs 1,000<br />

to Tshs 2,000. The price for fuelwood was reported to vary from 3,000 – 3,500 per cubic metre.<br />

6.4 Discussion<br />

The communities <strong>in</strong> <strong>the</strong> three village <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango depend on many<br />

tree-based products and services. The tree-based products obta<strong>in</strong>ed from village <strong>land</strong>scapes <strong>in</strong>clude local<br />

medic<strong>in</strong>es, timber, poles, fuelwoods, fruits and vegetables. A total <strong>of</strong> 56 species were mentioned by<br />

respondents from <strong>the</strong> three villages. Of <strong>the</strong>se only one species, Trilepsium madagascariensis was mentioned<br />

as be<strong>in</strong>g used <strong>in</strong> all three villages and 13 species were mentioned by respondents <strong>in</strong> two villages.<br />

Most species are collected from agforest plots. This <strong>in</strong>cludes patches <strong>of</strong> natural vegetation with<strong>in</strong> <strong>the</strong> mosaic <strong>of</strong><br />

agricultural <strong>land</strong> as well as areas where trees have been planted. Thirty species were mentioned as be<strong>in</strong>g<br />

used from forests <strong>of</strong> which five species were only collected from forests whilst <strong>the</strong> rest were also found <strong>in</strong><br />

„agr<strong>of</strong>orest‟ areas. Of those species that are only sourced from <strong>the</strong> village forest reserve, three are used as<br />

medic<strong>in</strong>es and two provide fruits. The results highlight <strong>the</strong> importance <strong>of</strong> <strong>the</strong> rema<strong>in</strong><strong>in</strong>g natural vegetation<br />

with<strong>in</strong> <strong>the</strong> agricultural mosaic as a source <strong>of</strong> timber and non-timber forest products <strong>in</strong>clud<strong>in</strong>g medic<strong>in</strong>al plants<br />

and food.<br />

37


7) Conclusions and recommendations<br />

This study recorded a total <strong>of</strong> 162 plant species (exclud<strong>in</strong>g plants recorded <strong>in</strong> <strong>the</strong> resource use survey) <strong>in</strong> <strong>the</strong><br />

<strong>different</strong> <strong>land</strong> <strong>cover</strong> <strong>types</strong> <strong>in</strong> <strong>the</strong> village <strong>land</strong>scapes <strong>of</strong> Misalai, Shambangeda and Kwatango (table 27). The list<br />

<strong>in</strong>cludes 102 tree species, 31 herb species, 17 shrub species and ten climbers.<br />

Table 27. Plant species recorded <strong>in</strong> <strong>the</strong> three village <strong>land</strong>scapes <strong>of</strong> <strong>the</strong> East Usambaras.<br />

Vegetation/<strong>land</strong> <strong>cover</strong> type Number <strong>of</strong> plant species<br />

recorded<br />

38<br />

Number <strong>of</strong> plant species<br />

recorded also <strong>in</strong> <strong>the</strong><br />

forests<br />

Village Forest Reserves 69 -<br />

Agr<strong>of</strong>orests 56 13<br />

Fallow <strong>land</strong>s 39 4<br />

Mixed farm<strong>in</strong>g plot 18 1<br />

A mosaic <strong>of</strong> fallow <strong>land</strong>, agr<strong>of</strong>orest and monoculture plot 9 1<br />

Monoculture and mixed farm<strong>in</strong>g plot 21 0<br />

Plantation 15 0<br />

Overall, this shows that <strong>the</strong> village forest reserves support a higher number <strong>of</strong> plant species compared to o<strong>the</strong>r<br />

non-reserved <strong>land</strong> <strong>cover</strong> <strong>types</strong>. Yet, a considerable number <strong>of</strong> plant species are also found <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orests,<br />

fallow <strong>land</strong>s, mixed farm<strong>in</strong>g plot as well as <strong>in</strong> <strong>the</strong> monoculture and mixed farm<strong>in</strong>g plot. In addition, some <strong>of</strong> <strong>the</strong><br />

plant species found <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orest and fallow <strong>land</strong>s are also <strong>in</strong> <strong>the</strong> forest reserves (Table 27).<br />

Many <strong>of</strong> <strong>the</strong> plant species are used by local people for various purposes, e.g. for timber, poles, fuelwood, as<br />

source <strong>of</strong> cash, and most importantly for medic<strong>in</strong>e. The majority <strong>of</strong> <strong>the</strong> species used by villagers were found <strong>in</strong><br />

<strong>the</strong> agr<strong>of</strong>orests, forest reserves, fallow <strong>land</strong>s and mixed farm<strong>in</strong>g plots. This shows that a considerable number<br />

<strong>of</strong> plant species that are vital for support<strong>in</strong>g <strong>the</strong> local livelihoods are found outside <strong>the</strong> formally protected areas.<br />

The survey recorded one East Usambara endemic plant species, Cynometra engleri. It was recorded <strong>in</strong> <strong>the</strong><br />

Kwatango village forest reserve. In addition, three Eastern Arc endemic plants were recorded: Alsodeiopsis<br />

schumannii (<strong>in</strong> agr<strong>of</strong>orests), Aoran<strong>the</strong> penduliflora (<strong>in</strong> agr<strong>of</strong>orests) and Drypetes gerrard<strong>in</strong>oides (<strong>in</strong> village<br />

forest reserve).The Eastern Arc near-endemics <strong>in</strong>clude Allanblackia stuhlmannii (<strong>in</strong> village forest reserves and<br />

agr<strong>of</strong>orests), Carvalhoa campanulata (<strong>in</strong> village forest reserve), Cephalosphaera usambarensis (<strong>in</strong> village<br />

forest reserves), Dasylepis <strong>in</strong>tegra (<strong>in</strong> village forest reserve), Dialium holtzii (<strong>in</strong> village forest reserve and mixed<br />

farm<strong>in</strong>g), Mesogyne <strong>in</strong>signis (<strong>in</strong> village forest reserve) and Pouteria alnifolia (<strong>in</strong> village forest reserve).<br />

Threatened plant species, classified as vulnerable <strong>in</strong> <strong>the</strong> most recent IUCN Red List (2010), <strong>in</strong>cluded <strong>the</strong> East<br />

Usamabra endemic species. In addition, <strong>the</strong>y <strong>in</strong>cluded Allanblackia stuhlmannii (<strong>in</strong> village forest reserves and<br />

agr<strong>of</strong>orests), Alsodeiopsis schumannii (<strong>in</strong> agr<strong>of</strong>orests), Aoran<strong>the</strong> penduliflora (<strong>in</strong> agr<strong>of</strong>orests), Cephalosphaera<br />

usambarensis (<strong>in</strong> village forest reserves), Dasylepis <strong>in</strong>tegra (<strong>in</strong> village forest reserves) Dialium holtzii (<strong>in</strong> village<br />

forest reserve and mixed farm<strong>in</strong>g), Drypetes gerrard<strong>in</strong>oides (village forest reserve), Mesogyne <strong>in</strong>signis (<strong>in</strong><br />

village forest reserve) and possibly Pavetta abyss<strong>in</strong>ica var. usambarica (village forest reserve).<br />

In terms <strong>of</strong> bird diversity, <strong>the</strong> village <strong>land</strong>scapes appeared to support a high number <strong>of</strong> species: 88 species<br />

were recorded, <strong>in</strong>clud<strong>in</strong>g <strong>the</strong> critically endangered Long-billed tailorbird Artisonis moreaui, recorded <strong>in</strong> <strong>the</strong><br />

agr<strong>of</strong>orest. O<strong>the</strong>r threatened bird species <strong>in</strong>cluded Amani sunbird (Anthreptes pallidigaster), recorded <strong>in</strong> a<br />

mosaic <strong>of</strong> fallow <strong>land</strong>, agr<strong>of</strong>orest and monoculture, banded green sunbird (Anthreptes rubritorques) <strong>in</strong> <strong>the</strong><br />

agr<strong>of</strong>orest, Sou<strong>the</strong>rn banded snake eagle (Circaetus fasciolatus) <strong>in</strong> a mosaic <strong>of</strong> fallow <strong>land</strong>, agr<strong>of</strong>orest and


monoculture and Fischer‟s turaco (Tauraco fischeri), recorded <strong>in</strong> agr<strong>of</strong>orest, fallow <strong>land</strong> and mixed farm<strong>in</strong>g<br />

plots.<br />

The banded green sunbird Anthreptes rubritorques was <strong>the</strong> only bird species recorded that is endemic to <strong>the</strong><br />

Eastern Arc Mounta<strong>in</strong>s. The bird was recorded <strong>in</strong> <strong>the</strong> agr<strong>of</strong>orest sites <strong>of</strong> Misalai and Shambangeda village<br />

<strong>land</strong>scapes. Eastern Arc near-endemic bird species recorded <strong>in</strong>cluded Andropadus masukuensis, Anthreptes<br />

pallidigaster, Batis mixta, Poeoptera kenricki, Stactolaema olivacea and Artisornis moreaui.<br />

In terms <strong>of</strong> rare mammal species, <strong>the</strong> vulnerable species - black and rufous sengi (Rhynchocyon petersi) - was<br />

recorded <strong>in</strong>side <strong>the</strong> forest reserves. This species is also near-endemic to <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s.<br />

In conclusion, <strong>the</strong> results <strong>of</strong> <strong>the</strong> study <strong>in</strong>dicate that <strong>the</strong> village <strong>land</strong>scapes <strong>in</strong> <strong>the</strong> East Usambaras support<br />

considerable biodiversity resources. These resources are important for conservation and for support<strong>in</strong>g <strong>the</strong><br />

livelihoods <strong>of</strong> local people. Apart from <strong>the</strong> village forest reserves, <strong>the</strong> o<strong>the</strong>r <strong>land</strong> use <strong>types</strong>, such as agr<strong>of</strong>orests<br />

and fallow <strong>land</strong>, support many valuable species.<br />

The results also suggest that many <strong>of</strong> <strong>the</strong> plant and vertebrate species endemic to <strong>the</strong> East Usambara may be<br />

restricted to <strong>the</strong> Government Forest and Nature Reserves <strong>the</strong>reby emphasiz<strong>in</strong>g <strong>the</strong> importance <strong>of</strong> <strong>in</strong>vest<strong>in</strong>g <strong>in</strong><br />

<strong>the</strong> conservation <strong>of</strong> <strong>the</strong> exist<strong>in</strong>g protected areas.<br />

The results highlight <strong>the</strong> importance <strong>of</strong> tak<strong>in</strong>g a <strong>land</strong>scape approach to conservation whereby conservation<br />

<strong>values</strong> should be recognized and enhanced across all <strong>land</strong> uses. Whilst protected areas, <strong>in</strong>clud<strong>in</strong>g village<br />

forest reserves, will cont<strong>in</strong>ue to harbor <strong>the</strong> vast majority <strong>of</strong> species <strong>in</strong> an area such as <strong>the</strong> East Usambaras,<br />

areas <strong>of</strong> agr<strong>of</strong>orestry can play an important role <strong>in</strong> provid<strong>in</strong>g habitat and corridors for some species.<br />

39


8) References<br />

Baker N.E. & Baker E.M. (2002) Important Bird Areas <strong>in</strong> Tanzania. A first <strong>in</strong>ventory. Wildlife Conservation<br />

Society <strong>of</strong> Tanzania. Dar es Salaam. Tanzania.<br />

Burgess N.D., Butynski T.M., Cordeiro N.J., Doggart N., Fjeldsa J., Howell K.M., Kilahama F., Loader S.P.,<br />

Lovett J.C., Mbilnyi B, Menegon M., Moyer D.C., Nashanda E., Perk<strong>in</strong> A., Rovero F., Stanley W.T. &<br />

Stuart S.N. (2007) The <strong>biological</strong> importance <strong>of</strong> <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s <strong>of</strong> Tanzania and Kenya.<br />

Biological Conservation 134: 209 - 231.<br />

Forestry & Beekeep<strong>in</strong>g Division (2006) Forest area basel<strong>in</strong>e for <strong>the</strong> Eastern Arc Mounta<strong>in</strong>s. Compiled by<br />

Mbil<strong>in</strong>yi, B. P., Malimbwi, R.E., Shemwetta, D.T.K., Songorwa, E., Zahabu, E., Katani, J.Z. & Kashaigili,<br />

J. for Conservation and Management <strong>of</strong> <strong>the</strong> Eastern Arc Mounta<strong>in</strong> Forests, Forestry and Beekeep<strong>in</strong>g<br />

Division, Morogoro. 60 pp.<br />

Hamilton, A.C. (1989) The place and <strong>the</strong> problem. a survey <strong>of</strong> forest <strong>types</strong> on <strong>the</strong> East Usambaras us<strong>in</strong>g <strong>the</strong><br />

variable-area tree plot method. In A.C. Hamilton & R. Bensted-Smith (eds.). Forest conservation <strong>in</strong> <strong>the</strong><br />

East Usambara Mounta<strong>in</strong>s Tanzania. IUCN, G<strong>land</strong>. Pp 213-226.<br />

ICRAF (2008) Integrat<strong>in</strong>g Livelihoods and Multiple Biodiversity Values <strong>in</strong> Landscape Mosaics: field methods.<br />

86 pp.<br />

IUCN (2010) 2010 IUCN Red List <strong>of</strong> Threatened Species. Available at: www.iucnredlist.org. Downloaded on<br />

May 2010.<br />

Lovett, J.C. (1985) An overview <strong>of</strong> <strong>the</strong> moist forests <strong>of</strong> Tanzania. Research Monographs <strong>of</strong> <strong>the</strong> Tanzania<br />

National Scientific Research Council, Dar es Salaam.<br />

Rovero, F., (2010). Mammals. In: Doggart, N., C. Leonard, A. Perk<strong>in</strong>, M. Menegon and F. Rovero (2010).<br />

Report on a survey <strong>of</strong> <strong>the</strong> vertebrate biodiversity and forest status <strong>of</strong> <strong>the</strong> Rubeho Mounta<strong>in</strong>s. TFCG Technical<br />

Paper No 19. DSM, Tz. 1 - 79 p<br />

40


Appendix 1. Habitat details for <strong>the</strong> vegetation plots <strong>in</strong> <strong>the</strong> East Usambaras<br />

Village<br />

Veg<br />

Plot#<br />

Vegetation/L<br />

and Use<br />

Type Altitude Coord<strong>in</strong>ates<br />

Misalai M1 Forest 1212 0458951/9445932<br />

Misalai M2 Agr<strong>of</strong>orestry<br />

1125 -<br />

1139<br />

Misalai M3 Fallow <strong>land</strong> 958 - 964<br />

Misalai M4<br />

Monoculture+<br />

Mixed farm<strong>in</strong>g 982 -1026<br />

Shambangeda S1 Forest 971 0459231/9440838<br />

0459964/9446401;<br />

0460167/9446433 VF, GLS<br />

SUS with<br />

>50%<br />

0459623/9444539; small<br />

0459751/9444688 valley >50%<br />

0459039/9443745,<br />

0458889/9443869 SMS >50%<br />

0469746/9446451,<br />

0469745/9446645 GUS<br />

41<br />

Topogra<br />

phy<br />

Ridge<br />

GL SL CC Aspect<br />

topo/SUS >50% >50% >50% N-S<br />

GUS+SU<br />

S<br />

Shambangeda S2 Agr<strong>of</strong>orestry<br />

Fallow <strong>land</strong>,<br />

Agr<strong>of</strong>orestry<br />

887-937<br />

0458710/9440288,<br />

0458552/9440183 GMS >50% >50%<br />

Shambangeda S3 &Monoculture 968 0458786/9442508 SMS >50% >50%<br />

Kwatango K1 Agr<strong>of</strong>orestry 179-211<br />

Kwatango K2 Forest 203-233<br />

0470734/9446282,<br />

0470744/9446087 GLS/Flat >50% >50%<br />

10 -<br />

50% >50% E-W<br />

10 -<br />

50% 0 E-W<br />

10 -<br />

50% 0 SE-NW<br />

10 -<br />

50% >50% >50% NW-SE<br />

10-<br />

50% >50% >50% N-S<br />

Signs <strong>of</strong><br />

past use<br />

Shrub<br />

clearance<br />

Previously<br />

cultivated<br />

area<br />

The village<br />

forest is<br />

encroached<br />

<strong>in</strong> <strong>the</strong><br />

northwestern<br />

part <strong>of</strong> <strong>the</strong><br />

forest<br />

Features <strong>of</strong><br />

<strong>in</strong>terest<br />

10-<br />

50% SW-NE<br />

Timber<br />

Close to river<br />

10-<br />

harvest<strong>in</strong>g<br />

50% N-S (occassional)<br />

Pitsaw<strong>in</strong>g <strong>of</strong><br />

10-<br />

Milicia<br />

50% N-S excelsa<br />

The eastern<br />

and no<strong>the</strong>rn<br />

forest<br />

boundaries<br />

are closer to<br />

rubber<br />

plantation


Village<br />

Kwatango K3<br />

Veg<br />

Plot#<br />

Kwatango K4 Mixed farm<strong>in</strong>g 178-198<br />

Kwatango K5<br />

Key:<br />

GL = Ground layer<br />

SL = Shrub layer<br />

CC = Canopy <strong>cover</strong><br />

SUS = Steep uppper slope<br />

VF = Valley forest<br />

GLS = Gentle lower<br />

slope<br />

SMS = Steep mid slope<br />

GUS = Gentle upper slope<br />

GMS = Gentle mid slope<br />

N-S = North-South<br />

E-W = East-West<br />

SE-NW = South-east North-west<br />

NW-SE = North-west South-east<br />

SW-NE = South-west North-east<br />

Vegetation/L<br />

and Use<br />

Topogra<br />

Type Altitude Coord<strong>in</strong>ates phy GL SL CC Aspect<br />

Fallow <strong>land</strong><br />

10-<br />

(old) 243 0470745/9447458 GLS >50% >50% 50% E-W<br />

0471931/9443422,<br />

0471735/9443403 GUS >50% >50%<br />

Teak<br />

plantation 186 0471310/9445254 GUS >50% >50%<br />

42<br />

10-<br />

50% E-W<br />

10-<br />

50% E-W<br />

Signs <strong>of</strong><br />

past use<br />

Pole cutt<strong>in</strong>g<br />

especially on<br />

<strong>the</strong> road<br />

periphery<br />

Features <strong>of</strong><br />

<strong>in</strong>terest


Appendix 2. List <strong>of</strong> plants found <strong>in</strong> <strong>the</strong> Misalai, Shambangeda and Kwatango villages’ <strong>land</strong>scapes.<br />

Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 1X40 Forest Acanthaceae (H) Isoglosa lactea 0.2 0.6<br />

Misalai M1 1X40 Forest Acanthaceae (H) Isoglosa lactea 1.1 1<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Acanthaceae (H) Isoglosa lactea<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Acanthaceae (H) Justicia sp 0.2 0.3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Acanthaceae (H) Justicia sp 0.2 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Acanthaceae (H) Justicia sp 0.2 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Acanthaceae (H) Justicia sp 2.1 2<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Acanthaceae (H) Justicia sp<br />

Misalai M3 1X40 Fallow <strong>land</strong> Acanthaceae (H) Justicia sp (2)<br />

Kwatango K2 1X40 Forest Acanthaceae (S) Sclerochiton sp 0.4 1.5<br />

Kwatango K2 1X40 Forest Acanthaceae (S) Sclerochiton sp 1.2 2<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 0.3 0.5<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 0.4 1<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 0.5 0.6<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 0.5 1<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 0.5 1.2<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 1 0.6<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 1 1<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 1.2 1<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 1.2 1.5<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 1.3 1<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongate 1.5 2<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongata 0.2 1<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongata 0.1 0.3<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongata (50) 0.2 1.5<br />

Misalai M1 1X40 Forest Acanthaceae (S) Whitfieldia elongata (51) 0.3 1<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Acanthaceae (S) Whitfieldia elongata (51)<br />

Misalai M3 1X40 Fallow <strong>land</strong> Adiantaceae (F) Pteris sp (17)<br />

43


Village<br />

Plot<br />

number<br />

Sub-plot size (m) Land <strong>cover</strong> type<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%)<br />

Adiantaceae (F) Pteris sp (29)<br />

Shambangeda S3 1X40<br />

&Monoculture (50%) Adiantaceae (F) Pteris sp(16)<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Adiantaceae (F) Pteris sp(44)<br />

Kwatango K5 10X200 Plantation Alariaceae Cussonia zimmermanii 30.7 12<br />

Kwatango K5 10X200 Plantation Alariaceae Cussonia zimmermanii 44 21<br />

Misalai M1 10X200 Forest Alariaceae Polycias fulva 120 50<br />

Shambangeda S1 10X200 Forest Alariaceae Polyscias fulva 31 15<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Anacardiaceae Lannea stuhlmannii 0.2 1<br />

Kwatango K5 1X40 Plantation Anacardiaceae Lannea stuhlmannii 0.2 1.25<br />

Kwatango K5 10X200 Plantation Anacardiaceae Lannea stuhlmannii 30 18<br />

Kwatango K5 10X200 Plantation Anacardiaceae Lannea stuhlmannii 35 20<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Anacardiaceae Mangifera <strong>in</strong>dica 74.5 30<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.1 0.5<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.1 0.6<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.2 0.75<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.2 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.3 0.25<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.3 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.3 1<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.3 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.4 0.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.5 1.5<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.5 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.6 0.6<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.6 1.5<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.6 2<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.6 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.7 0.6<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.7 2.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.8 0.6<br />

44


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.8 1.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.9 0.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 0.9 0.75<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.1 0.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.1 2.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.2 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.2 0.6<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.2 1.5<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.2 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.2 2.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.3 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.3 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.3 3.5<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.5 1.25<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.5 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.6 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.6 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.6 4.4<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.7 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.7 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.8 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.8 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.9 3.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 1.9 4<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 2 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 2 2<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 2 3<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 2 3<br />

Shambangeda S1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 2 3.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 2.2 3.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 3.5 5<br />

Misalai M1 5X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 29 20<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 30 25<br />

45


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 30.4 12<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 33.6 20<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 34.4 20<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 36.7 28<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 37 20<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 38.3 25<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 39.5 18<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 40 15<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 40 20<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 43.3 15<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 44 15<br />

Misalai M1 10X200 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis 45 35<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.2 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.3 0.6<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.3 0.75<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.4 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.4 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.5 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.6 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.8 0.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 0.9 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1 0.75<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1.1 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1.1 1.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1.2 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1.3 2.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1.7 4<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (2) 1.9 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 0.1 0.3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 0.2 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 0.4 0.6<br />

46


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 1.1 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 1.2 2<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 1.5 1.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 1.5 3<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3) 1.6 2.5<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (3)<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (4) 0.2 0.6<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (4) 0.7 0.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (4) 1.5 2.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (4) 2 3.5<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (6) 0.9 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (9) 1 1<br />

Misalai M1 1X40 Forest Anacardiaceae Sor<strong>in</strong>deia madagascariensis (9) 1 1.5<br />

Kwatango K5 1X40 Plantation Annonaceae Annona senegalensis 3.3 2.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Annonaceae Annona sp 2.1 3.5<br />

Kwatango K2 1X40 Forest Annonaceae Uvaria angolensis 1.3 1<br />

Shambangeda S1 1X40 Forest Apocyanaceae Tabernaemontana pachysiphon 0.3 2<br />

Shambangeda S1 1X40 Forest Apocyanaceae Tabernaemontana pachysiphon 4 4<br />

Shambangeda S1 1X40 Forest Apocyanaceae Tabernaemontana pachysiphon 4.3 5<br />

Shambangeda S1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 0.1 0.3<br />

Shambangeda S1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 0.2 0.5<br />

Shambangeda S1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 0.2 0.6<br />

Shambangeda S1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 0.3 1.5<br />

Misalai M1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 0.6 1<br />

Misalai M1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 1 0.75<br />

Shambangeda S1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 6.6 4<br />

Shambangeda S1 5X40 Forest Apocynaceae Tabernaemontana pachysiphon<br />

Tabernaemontana pachysiphon<br />

11.5 10<br />

Shambangeda S1 1X40 Forest Apocynaceae (2) 0.4 2<br />

Shambangeda S1 1X40 Forest Apocynaceae Tabernaemontana pachysiphon 0.2 0.3<br />

Shambangeda S1 1X40 Forest Apocynaceae ( C) Landolphia buchananii<br />

Kwatango K2 1X40 Forest Apocynaceae ( C) Landolphia buchananii<br />

Misalai M1 1X40 Forest Apocynaceae ( C) Landolphia buchananii (2) 0.1 0.3<br />

47


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Shambangeda S1 1X40 Forest Apocynaceae (S) Carvalhoa campanulata 0.1 0.5<br />

Shambangeda S1 1X40 Forest Apocynaceae (S) Carvalhoa campanulata 1.6 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Apocynaceae (S) Schizozygia c<strong>of</strong>faioides 0.4 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Apocynaceae (S) Schizozygia c<strong>of</strong>faioides 0.5 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Apocynaceae (S) Schizozygia c<strong>of</strong>faioides<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Apocynaceae (S) Schizozygia c<strong>of</strong>faioides 0.4 0.4<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Apocynaceae (S) Schizozygia c<strong>of</strong>faioides (2) 0.6 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Apocynaceae (S) Schizozygia c<strong>of</strong>faioides (3) 0.3 0.6<br />

Misalai M4 1X40<br />

Monoculture & mixed<br />

farm<strong>in</strong>g Araceae (C) Culcasia sp (2)<br />

Kwatango K3 5X40 Fallow <strong>land</strong> Araliaceae Cussonia zimmermanii 12 8<br />

Kwatango K3 5X40 Fallow <strong>land</strong> Araliaceae Cussonia zimmermanii 18<br />

Collected<br />

10<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Aspleniaceae (F) Asplenium sp<br />

5877<br />

Shambangeda S1 1X40 Forest Aspleniaceae (F) Asplenium sp<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Aspleniaceae (F) Asplenium sp (36)<br />

Misalai M3 1X40 Fallow <strong>land</strong> Asteraceae (H) Bidens pilosa<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceae (H) Bidens pilosa (14)<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (H) Bidens pilosa (4)<br />

Shambangeda S3 1X40<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%)<br />

&Monoculture (50%) Asteraceae (H) Bidens pilosa (5)<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Asteraceae (H) Bothriocl<strong>in</strong>e sp<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Asteraceae (H) Bothriocl<strong>in</strong>e sp<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Asteraceae (H) Bothriocl<strong>in</strong>e sp (3)<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g<br />

Monoculture&Mixed<br />

Asteraceae (H) Bothriocl<strong>in</strong>e sp (4)<br />

Misalai M4 1X40<br />

farm<strong>in</strong>g Asteraceae (H) Conyza sp<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Asteraceae (H) Conyza sp (12)<br />

Shambangeda S3 1X40<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%)<br />

&Monoculture (50%) Asteraceae (H) Conyza sp (3)<br />

48


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M3 1X40 Fallow <strong>land</strong> Asteraceae (H) Conyza sp (34)<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Asteraceae (H) Conyza sp (38)<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Asteraceae (H) Conyza sp (4)<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceae (H) Conyza sp (5)<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Asteraceae (H) Emilia sp (3)<br />

Misalai M3 1X40 Fallow <strong>land</strong> Asteraceae (H) Helichrysium odoratissimum<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Asteraceae (H) Sonchus sp (2)<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g<br />

Monoculture&Mixed<br />

Asteraceae (S) Vernonia lasiopus 0.1 1<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus 0.2 1<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus 1.2 2<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g<br />

Monoculture&Mixed<br />

Asteraceae (S) Vernonia lasiopus 1.3 2.5<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus 1.3 3<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus 1.4 2.5<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g<br />

Monoculture&Mixed<br />

Asteraceae (S) Vernonia lasiopus<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus (2) 0.3 2<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus (3) 0.3 0.7<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia lasiopus (3)<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceae (S) Vernonia myriantha 0.1 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceae (S) Vernonia myriantha 0.1 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceae (S) Vernonia myriantha 0.1 0.3<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia myriantha 0.1 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Asteraceae (S) Vernonia myriantha 0.1 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Asteraceae (S)<br />

49<br />

Vernonia myriantha 0.2 0.3


Village<br />

Plot<br />

number<br />

Misalai M4 1X40<br />

Sub-plot size (m) Land <strong>cover</strong> type<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia myriantha 0.2 1<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia myriantha 0.2 1.5<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceae (S) Vernonia myriantha 0.3 0.4<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia myriantha 0.6 1.5<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Asteraceae (S) Vernonia myriantha 2 1.5<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Asteraceare (S) Vernonia myriantha 0.2 0.3<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Basalm<strong>in</strong>aceae (H) Impatiens sp (3)<br />

Kwatango K2 1X40 Forest Bignoniaceae Markhamia sp 2.5 3<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Bombacaceae Ceiba pentandra 60 50<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Bombacaceae Ceiba pentandra 71 45<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Bromeliaceae (H) Ananas comosus<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Bromeliaceae (H) Ananas comosus<br />

Kwatango K5 1X40 Plantation Bursaraceae Commiphora africana 2.4 2.5<br />

Kwatango K5 10X200 Plantation Bursaraceae Commiphora africana 35 12<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra engleri 0.2 1<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra engleri 2 4<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra engleri 2.8 5<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra engleri 4 7<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.1 0.6<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.2 0.75<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.2 1<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.2 2<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.3 0.3<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.3 1<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.4 1<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 0.6 2.5<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 30 25<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 36.5 27<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 40 30<br />

50


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Cynometra longipedicellata 49 30<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Cynometra sp 130 45<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 0.1 0.3<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 0.1 0.3<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 0.1 0.6<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 0.2 0.3<br />

Kwatango K2 1X40 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 0.2 0.6<br />

Kwatango K2 5X40 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 21.4 20<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 30 20<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 30 25<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 30 25<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 30 30<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 31 15<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 31 20<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 31 25<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 31 28<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 34 20<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 38 30<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 40.7 35<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 41.5 35<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 45 28<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 55 40<br />

Kwatango K2 10X200 Forest Caesalp<strong>in</strong>iaceae Dialium holtzii 79.3 30<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Caesalp<strong>in</strong>iaceae Dialium holtzii 0.1 0.3<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Caesalp<strong>in</strong>iaceae Dialium holtzii (2) 0.2 0.3<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Caesalp<strong>in</strong>iaceae Dialium holtzii (3) 0.2 0.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Caesalp<strong>in</strong>iaceae Cassia abbreviata (2) 0.3 1<br />

Kwatango K2 10X200 Forest Cecropiaceae Dialium holtzii 87 45<br />

Misalai M2 5X40 Agr<strong>of</strong>orest Cecropiaceae Myrianthus holstii 10 6<br />

Misalai M1 5X40 Forest Cecropiaceae Myrianthus holstii 11.3 10<br />

Misalai M2 5X40 Agr<strong>of</strong>orest Cecropiaceae Myrianthus holstii 11.7 6<br />

Misalai M1 5X40 Forest Cecropiaceae Myrianthus holstii 12.8 20<br />

Misalai M1 5X40 Forest Cecropiaceae Myrianthus holstii 16.3 15<br />

51


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 5X40 Forest Cecropiaceae Myrianthus holstii 17 20<br />

Misalai M1 5X40 Forest Cecropiaceae Myrianthus holstii 25.3 8<br />

Misalai M1 10X200 Forest Cecropiaceae Myrianthus holstii 31 20<br />

Shambangeda S1 10X200 Forest Cecropiaceae Myrianthus holstii 31.3 15<br />

Shambangeda S1 10X200 Forest Cecropiaceae Myrianthus holstii 38 25<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Cecropiaceae Myrianthus holstii 41.9 20<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Cecropiaceae Myrianthus holstii 42 20<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Cecropiaceae Myrianthus holstii 44 30<br />

Misalai M1 10X200 Forest Cecropiaceae Myrianthus holstii 54 25<br />

Misalai M1 10X200 Forest Cecropiaceae Myrianthus holstii 55.4 35<br />

Shambangeda S1 1X40 Forest Celastraceae<br />

Commel<strong>in</strong>aceae<br />

Maytenus acum<strong>in</strong>ata 0.5 1<br />

Misalai M3 1X40 Fallow <strong>land</strong><br />

(H) Commel<strong>in</strong>a benghalensis<br />

Kwatango K2 1X40 Forest Connaraceae ( C) Agelaea sp<br />

Shambangeda S1 1X40 Forest Connaraceae ( C) Agelaea pentagyna<br />

Misalai M1 1X40 Forest Connaraceae ( C) Agelaea pentagyna 1 1.5<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Convulvaceae (H) Ipomoea batatas<br />

Misalai M1 1X40 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 1.5 2<br />

Misalai M1 1X40 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 1.8 2<br />

Misalai M1 1X40 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 2 2<br />

Shambangeda S1 1X40 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 2.4 1<br />

Misalai M1 1X40 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 2.8 4<br />

Shambangeda S1 5X40 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 17.7 10<br />

Shambangeda S1 10X200 Forest Crysobalanaceae Par<strong>in</strong>ari excelsa 110 50<br />

Shambangeda S1 10X200 Forest Crysobalanaceae<br />

Dichapetalaceae<br />

Par<strong>in</strong>ari excelsa 125 60<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g (C) Dichapetalum sp (2)<br />

Misalai M1 1X40 Forest Dracaenacea (S) Dracaena laxissima 1.6 2<br />

Misalai M1 1X40 Forest Dracaenacea (S) Dracaena laxissima 1.5 2.5<br />

Shambangeda S1 1X40 Forest Dracaenaceae (S) Dracaena laxissima 0.1 0.6<br />

Shambangeda S1 1X40 Forest Dracaenaceae (S) Dracaena laxissima 0.2 1<br />

Shambangeda S1 1X40 Forest Dracaenaceae (S) Dracaena laxissima 0.3 1<br />

Shambangeda S1 1X40 Forest Dracaenaceae (S) Dracaena laxissima 0.4 1<br />

Misalai M1 1X40 Forest Dracaenaceae (S)<br />

52<br />

Dracaena laxissima 1.1 2


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 1X40 Forest Dracaenaceae (S) Dracaena laxissima (2) 1 2<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 0.1 0.3<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 0.1 0.6<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 0.2 1<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 0.3 0.6<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 0.5 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Ebenaceae Diospyros mespiliformis 1.2 0.3<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Ebenaceae Diospyros mespiliformis 1.3 0.6<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 2 3.5<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 2.1 3<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 2.2 2<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 2.2 3<br />

Kwatango K2 1X40 Forest Ebenaceae Diospyros mespiliformis 4.1 3.5<br />

Shambangeda S1 1X40 Forest Erythroxylaceae Erythroxylum emarg<strong>in</strong>atum 0.1 0.3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii 0.1 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii 0.2 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii 0.2 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii 0.4 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii 1.2 2.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii 0.3 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii (2) 0.1 6<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii (2) 1.3 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii (3) 1.9 3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii (4) 0.3 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii (6) 0.3 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Acalypha volkensii (7) 0.2 2<br />

Kwatango K2 1X40 Forest Euphorbiaceae Alchornea hirtellus 0.2 1.5<br />

Kwatango K2 1X40 Forest Euphorbiaceae Alchornea hirtellus 0.3 2<br />

Kwatango K2 1X40 Forest Euphorbiaceae Alchornea hirtellus 0.5 3<br />

Kwatango K2 1X40 Forest Euphorbiaceae Alchornea hirtellus 2.3 3<br />

Kwatango K2 1X40 Forest Euphorbiaceae Alchornea hirtellus 3.1 3<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae Bridelia micrantha 0.1 0.5<br />

53


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae Bridelia micrantha 0.1 0.5<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae Bridelia micrantha 0.1 0.5<br />

Shambangeda S3 1X40<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%)<br />

&Monoculture (50%) Euphorbiaceae Bridelia micrantha 0.1 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Euphorbiaceae Bridelia micrantha 0.3 0.6<br />

Shambangeda S3 1X40<br />

Monoculture (50%)<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Euphorbiaceae Bridelia micrantha 0.3 1<br />

Shambangeda S3 1X40<br />

Monoculture (50%) Euphorbiaceae Bridelia micrantha 0.3 1.25<br />

Misalai M3 1X40 Fallow <strong>land</strong> Euphorbiaceae Bridelia micrantha 0.4 2<br />

Misalai M3 1X40 Fallow <strong>land</strong> Euphorbiaceae Bridelia micrantha<br />

Misalai M4 1X40<br />

Monoculture & Mixed<br />

farm<strong>in</strong>g Euphorbiaceae Bridelia micrantha<br />

Misalai M3 1X40 Fallow <strong>land</strong> Euphorbiaceae Bridelia micrantha (2) 2 2<br />

Kwatango K2 1X40 Forest Euphorbiaceae Drypetes gerrard<strong>in</strong>oides 0.2 1<br />

Shambangeda S1 10X200 Forest Euphorbiaceae Drypetes usambarica 37.9 15<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Fluggea virosa 0.1 0.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Fluggea virosa 2.1 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Euphorbiaceae Fluggea virosa 2.1 2<br />

Kwatango K5 1X40 Plantation Euphorbiaceae Fluggea virosa 3.1 5<br />

Shambangeda S1 5X40 Forest Euphorbiaceae Macaranga kilimandscharica 17.7 25<br />

Misalai M1 10X200 Forest Euphorbiaceae Macaranga kilimandscharica 32.3 25<br />

Shambangeda S1 10X200 Forest Euphorbiaceae Macaranga kilimandscharica 38 32<br />

Misalai M1 10X200 Forest Euphorbiaceae Macaranga kilimandscharica 46.3 35<br />

Misalai M1 10X200 Forest Euphorbiaceae Macaranga kilimandscharica 48.1 35<br />

Misalai M1 10X200 Forest Euphorbiaceae Macaranga kilimandscharica 54.5 35<br />

Shambangeda S1 10X200 Forest Euphorbiaceae Macaranga kilimandscharica 59 30<br />

Misalai M3 10X200 Fallow <strong>land</strong> Euphorbiaceae Shirakiopsis elliptica 32 10<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Euphorbiaceae Shirakiopsis elliptica 104 45<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae (H) Phyllanthus sp 0.1 0.3<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae (H) Phyllanthus sp 0.1 0.4<br />

54


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.2 0.6<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.2 0.6<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.3 0.6<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.3 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.3 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.3 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.4 1.5<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.5 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.7 1.5<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 0.9 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 1.1 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 1.1 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 1.6 2<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 1.9 2<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 2 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 2.1 3<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 2.2 1<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp 2.3 3<br />

Kwatango K2 1X40 Forest Euphorbiaceae (S) Acalypha sp (2) 1 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong><br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Euphorbiaceae (S) Erythrococca fischeri 0.2 1<br />

Shambangeda S3 1X40<br />

Monoculture (50%)<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Euphorbiaceae (S) Manihot esculenta 0.1 0.3<br />

Shambangeda S3 1X40<br />

Monoculture (50%) Euphorbiaceae (S) Manihot esculenta 0.2 0.3<br />

Shambangeda S3 1X40<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Monoculture (50%) Euphorbiaceae (S) Manihot esculenta 0.3 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 0.6 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 0.7 1.5<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 0.7 1.5<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 0.8 1<br />

55


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 0.8 2<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 0.9 2<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Euphorbiaceae (S) Manihot esculenta 1 2<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 1.2 0.1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Euphorbiaceae (S) Manihot esculenta 1.3 0.4<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Euphorbiaceae (S) Manihot esculenta 1.5 2<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Euphorbiaceae (S) Manihot esculenta 1.5 2<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Euphorbiaceae (S) Manihot esculenta 1.6 2<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Euphorbiaceae (S) Manihot esculenta 2.5 2<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Euphorbiaceae (S) Manihot esculenta (2) 0.4 1<br />

Misalai M1 1X40 Forest Flacourtiacea Dasylepis <strong>in</strong>tegra 0.8 0.5<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Flacourtiacea Rawsonia reticulata 77 40<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Flacourtiacea Rawsonia reticulata 200 55<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Gram<strong>in</strong>ae (H) Saccharum <strong>of</strong>fic<strong>in</strong>arum<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.1 0.5<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.1 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.2 0.3<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.2 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.2 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.3 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.3 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.5 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.5 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.5 1<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 0.6 1.5<br />

Shambangeda S1 1X40 Forest Guttiferae Allanblackia stuhlmannii 2.3 3<br />

56


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Shambangeda S1 10X200 Forest Guttiferae Allanblackia stuhlmannii 54.1 25<br />

Shambangeda S1 10X200 Forest Guttiferae Allanblackia stuhlmannii 103.5 50<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Incac<strong>in</strong>aceae Alsodeiopsis schumannii 30 6<br />

Shambangeda S1 1X40 Forest Incac<strong>in</strong>aceae Leptaulus holstii 0.2 1<br />

Shambangeda S1 1X40 Forest Lamiaceae Ro<strong>the</strong>ca myricoides 0.1 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Lamiaceae (S) Hoslundia opposita 0.3 2<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Lamiaceae (H) Stachytapheta jamaicensis<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Lamiaceae (S) Hoslundia opposita 0.2 2<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Lauaraceae Persea americana 0.3 0.3<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Lauaraceae Persea americana 2.2 1.5<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Lauraceae Persea americana 1.5 1<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Lauraceae Persea americana<br />

Kwatango K2 10X200 Forest Loganiaceae Strychnos mitis 30 25<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Malvaceae Thespesia garckeana 0.1 0.3<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Malvaceae (H) Hibiscus sp (6)<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Melastomataceae<br />

Melastomataceae<br />

Dissotis rutondifolia<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest<br />

(H)<br />

Melastomataceae<br />

Clidemia hirta 0.1 0.4<br />

Misalai M2 1X40 Agr<strong>of</strong>orest<br />

(H)<br />

Melastomataceae<br />

Clidemia hirta (3)<br />

Misalai M3 1X40 Fallow <strong>land</strong><br />

(H)<br />

Melastomataceae<br />

Clidemia hirta (5)<br />

Misalai M3 1X40 Fallow <strong>land</strong><br />

(H) Dissotis rutondifolia (3)<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Meliaceae Cedrela odorata<br />

Pseudobersama<br />

2.9 1.5<br />

Kwatango K2 1X40 Forest Meliaceae<br />

mossambicensis<br />

Pseudobersama<br />

3 3.5<br />

Kwatango K2 1X40 Forest Meliaceae<br />

mossambicensis 4.2 6<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Meliaceae<br />

57<br />

Trichilia emetica 0.2 0.4


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Meliaceae Trichilia emetica 0.3 0.6<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Meliaceae Trichilia emetica 0.4 0.6<br />

Kwatango K5 10X200 Plantation Meliaceae Trichilia emetica 31 20<br />

Kwatango K5 10X200 Plantation Meliaceae Trichilia emetica 34 20<br />

Kwatango K5 10X200 Plantation Meliaceae Trichilia emetica 40 5<br />

Kwatango K5 10X200 Plantation Meliaceae Trichilia emetica 42.6 30<br />

Misalai M1 1X40 Forest Melianthaceae Bersama abyss<strong>in</strong>ica 0.8 0.5<br />

Misalai M1 1X40 Forest Melianthaceae Bersama abyss<strong>in</strong>ica 1.5 1.2<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Mimosaceae Albizia adianthifolia 45.5 35<br />

Misalai M1 1X40 Forest Mimosaceae Albizia gummifera 0.9 2<br />

Misalai M1 1X40 Forest Mimosaceae Albizia gummifera 1.1 2<br />

Misalai M1 1X40 Forest Mimosaceae Albizia gummifera 1.5 3<br />

Shambangeda S1 1X40 Forest Mimosaceae Albizia gummifera 6 3<br />

Misalai M1 10X200 Forest Mimosaceae Albizia gummifera 37.5 20<br />

Misalai M1 10X200 Forest Mimosaceae Albizia gummifera 50.5 45<br />

Misalai M1 10X200 Forest Mimosaceae Albizia gummifera 86 50<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Mimosaceae Albizia schimperiana 0.3 2.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Mimosaceae Albizia schimperiana 2.1 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Mimosaceae Albizia schimperiana 2.5 3<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Mimosaceae Albizia schimperiana 32 15<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Mimosaceae Albizia schimperiana 32 25<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Mimosaceae Albizia schimperiana 38 10<br />

Kwatango K5 1X40 Plantation Mimosaceae Albizia sp 4.1 4<br />

Kwatango K5 1X40 Plantation Mimosaceae Albizia sp 9 7<br />

Kwatango K5 10X200 Plantation Meliaceae Albizia sp 40 12<br />

Kwatango K5 5X40 Plantation Mimosaceae Albizia sp 11 8<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Mimosaceae Albizia sp<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Mimosaceae Cussonia zimmermanii 73 25<br />

Shambangeda S1 1X40 Forest Mimosaceae Newtonia buchananii 0.1 0.3<br />

Misalai M1 1X40 Forest Mimosaceae Newtonia buchananii 1 3<br />

Misalai M1 1X40 Forest Mimosaceae Newtonia buchananii 1.2 1<br />

Misalai M1 1X40 Forest Mimosaceae Newtonia buchananii 1.4 2<br />

Shambangeda S1 1X40 Forest Mimosaceae Newtonia buchananii 3 5<br />

58


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M1 1X40 Forest Mimosaceae Newtonia buchananii 5 5<br />

Misalai M1 10X200 Forest Mimosaceae Newtonia buchananii 90.5 55<br />

Misalai M1 1X40 Forest Monimiaceae Xymalos monospora 0.7 0.5<br />

Misalai M1 1X40 Forest Monimiaceae Xymalos monospora 0.7 1<br />

Misalai M1 5X40 Forest Monimiaceae Xymalos monospora 12.2 10<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Monimiaceae Xymalos monospora (2)<br />

Shambangeda S1 1X40 Forest Moraceae Antiaris toxicaria 0.1 0.3<br />

Shambangeda S1 1X40 Forest Moraceae Antiaris toxicaria 0.1 0.3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Antiaris toxicaria 0.2 1<br />

Shambangeda S1 1X40 Forest Moraceae Antiaris toxicaria 0.2 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Antiaris toxicaria 0.3 1.3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Antiaris toxicaria 1 1.5<br />

Shambangeda S1 1X40 Forest Moraceae Antiaris toxicaria 3.3 5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Antiaris toxicaria 5.4 1<br />

Shambangeda S1 10X200 Forest<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Moraceae Antiaris toxicaria 49 40<br />

Shambangeda S3 5X40<br />

Monoculture (50%)<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Moraceae Artocarpus heterophyllus 25 12<br />

Shambangeda S3 5X40<br />

Monoculture (50%) Moraceae Artocarpus heterophyllus 27.5 12<br />

Misalai M3 10X200 Fallow <strong>land</strong> Moraceae Artocarpus heterophyllus 81.2 15<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 0.1 1<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 0.3 2<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 0.5 2<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 0.7 2.5<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 0.9 3<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 3.2 5<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 3.7 5<br />

Kwatango K2 1X40 Forest Moraceae Bosqueiopsis gilletii 8.5 5<br />

Kwatango K2 5X40 Forest Moraceae Bosqueiopsis gilletii 10 10<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 0.2 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 0.2 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae<br />

59<br />

Ficus exasperata 0.2 1


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 0.3 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 0.4 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 0.6 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 1.1 2<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 1.5 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata 1.5 1.5<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata (2) 0.1 0.3<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata (2) 1.1 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata (2) 1.3 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata (3) 1.2 1<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Moraceae Ficus exasperata (5) 0.1 1<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Moraceae Ficus thonn<strong>in</strong>gii 36.8 22<br />

Misalai M1 10X200 Forest Moraceae Ficus thonn<strong>in</strong>gii 50 25<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 0.1 0.3<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 0.1 0.3<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 0.3 1<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 1.5 3<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 2.1 3<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 2.9 3<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 2.9 3<br />

Shambangeda S1 1X40 Forest Moraceae Mesogyne <strong>in</strong>signis 4.9 2<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Moraceae Milicia excelsa 0.1 0.3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Milicia excelsa 2.5 2<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Milicia excelsa 2.9 3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Milicia excelsa 3.5 4<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Moraceae Milicia excelsa 3.7 4<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Moraceae Milicia excelsa 12.5 1<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Moraceae Milicia excelsa 30 30<br />

Shambangeda S2 10X200 Agr<strong>of</strong>orest Moraceae Milicia excelsa 33.5 10<br />

Shambangeda S2 10X200 Agr<strong>of</strong>orest Moraceae Milicia excelsa 36.1 12<br />

Shambangeda S2 10X200 Agr<strong>of</strong>orest Moraceae Milicia excelsa 36.9 12<br />

Kwatango K4 10X200 Mixed farm<strong>in</strong>g Moraceae Milicia excelsa 39 23<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Moraceae Milicia excelsa 45 20<br />

60


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K4 10X200 Mixed farm<strong>in</strong>g Moraceae Milicia excelsa 45 25<br />

Kwatango K3 10X200 Fallow <strong>land</strong> Moraceae Milicia excelsa 49.4 30<br />

Misalai M3 10X200 Fallow <strong>land</strong> Moraceae Milicia excelsa 74.7 35<br />

Kwatango K4 10X200 Mixed farm<strong>in</strong>g Moraceae Milicia excelsa 77 25<br />

Misalai M3 10X200 Fallow <strong>land</strong> Moraceae Milicia excelsa 94.8 25<br />

Kwatango K1 10X200 Agr<strong>of</strong>orest Moraceae Trilepisium madagascariensis 33.5 20<br />

Shambangeda S1 10X200 Forest Moraceae Trilepisium madagascariensis 51.9 40<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Musaceae (H) Ensete ventricosa<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Musaceae (H) Musa sp (5)<br />

Misalai M1 10X200 Forest Myris<strong>in</strong>aceae Maesa lanceolata 33.9 20<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.1 0.3<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.1 0.6<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.1 0.6<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.2 0.6<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.2 0.75<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.2 1<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.2 1<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.3 1<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.3 2<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.4 1<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.7 2<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 0.8 3<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 1.8 1.5<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 3.5 4<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 5.1 5<br />

Shambangeda S1 1X40 Forest Myrsticaceae Cephalosphaera usambarensis 7 6<br />

Kwatango K2 1X40 Forest Ochnaceae Ochna thomasiana 2 3<br />

Misalai M1 1X40 Forest Olacaceae Strembosia scheffleri 0.8 1<br />

Kwatango K1 10X200 Agr<strong>of</strong>orest Palmae Elaeis gu<strong>in</strong>eensis 49 7<br />

Kwatango K2 1X40 Forest Papilionaceae Millettia usaramensis 0.2 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Papilionaceae Millettia usaramensis 2.2 2.5<br />

Kwatango K2 1X40 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 1.3 2<br />

Kwatango K2 1X40 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 9.2 6<br />

61


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K2 5X40 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 11.1 10<br />

Kwatango K2 5X40 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 13.7 16<br />

Kwatango K2 5X40 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 15.7 20<br />

Kwatango K2 10X200 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 31 25<br />

Kwatango K2 10X200 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 31 25<br />

Kwatango K2 10X200 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 32 35<br />

Kwatango K2 10X200 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 36 35<br />

Kwatango K2 10X200 Forest Papilionaceae Pterocarpus t<strong>in</strong>ctorius 80 35<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Papilionaceae (H) Desmodium repandum (2)<br />

Kwatango K5 1X40 Plantation Papilionaceae (S) Desmodium sp 0.1 0.75<br />

Kwatango K5 1X40 Plantation Papilionaceae (S) Desmodium sp (2) 0.1 0.5<br />

Misalai M3 1X40 Fallow <strong>land</strong> Passifloraceae (C ) Adenia gummifera<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 0.8 0.6<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 1.2 2<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 1.5 3<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 1.6 2<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 1.9 3.5<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 2 2.5<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 2.2 4.5<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 2.4 4<br />

Misalai M1 1X40 Forest Piperaceae (S) Piper capense 1.7 3<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Piperaceae (S) Piper capense (3)<br />

Shambangeda S1 1X40 Forest Poaceae (H) Olyra latifolia<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Poaceae (H) Oplismenus hirtellus (2)<br />

Misalai M3 1X40 Fallow <strong>land</strong> Poaceae (H) Panicum sp<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Poaceae (H) Panicum trichocladum<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Poaceae (H) Panicum trichocladum<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Poaceae (H) Panicum trichocladum<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Poaceae (H) Panicum trichocladum<br />

Kwatango K5 1X40 Plantation Poaceae (H) Panicum trichocladum<br />

62


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Shambangeda S3 1X40<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Monoculture (50%) Poaceae (H) Saccharum <strong>of</strong>fic<strong>in</strong>arum (37)<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Poaceae (H) Saccharum <strong>of</strong>fic<strong>in</strong>arum (39)<br />

Kwatango K5 1X40 Plantation<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Poaceae (H) Setaria megaphylla<br />

Shambangeda S3 1X40<br />

Monoculture (50%) Poaceae (H) Sorghum sp. (12)<br />

Misalai M3 1X40 Fallow <strong>land</strong> Poaceae (H) Sorghum sp. (8)<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Poaceae (H) Zea mays (47)<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Polygalaceae (H) Polygala sp<br />

Shambangeda S2 5X40 Agr<strong>of</strong>orest Protaceae Grevellia robusta 14 10<br />

Shambangeda S2 5X40 Agr<strong>of</strong>orest<br />

Fallow <strong>land</strong> (40%) &<br />

Agr<strong>of</strong>orest (10%) &<br />

Protaceae Grevellia robusta 18 15<br />

Shambangeda S3 5X40<br />

Monoculture (50%) Protaceae Grevellia robusta 28.3 15<br />

Shambangeda S2 10X200 Agr<strong>of</strong>orest Protaceae Grevellia robusta 30 15<br />

Misalai M4 5X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Protaceae Grevillea robusta 23 20<br />

Misalai M3 10X200 Fallow <strong>land</strong> Protaceae Grevillea robusta 30 12<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Rhamnaceae Maesopsis em<strong>in</strong>ii 30 30<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 31 35<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 32 25<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 32 35<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 35 10<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Rhamnaceae Maesopsis em<strong>in</strong>ii 36 40<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 37.2 55<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 37.9 35<br />

Misalai M2 10X200 Agr<strong>of</strong>orest Rhamnaceae Maesopsis em<strong>in</strong>ii 38.1 45<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 45.3 50<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 71 40<br />

Shambangeda S1 10X200 Forest Rhamnaceae Maesopsis em<strong>in</strong>ii 82.7 45<br />

Misalai M2 5X40 Agr<strong>of</strong>orest Rhamnaceae Maesopsis em<strong>in</strong>ii<br />

Misalai M3 1X40 Fallow <strong>land</strong> Rosaceae ( C) Rubus sp. (20)<br />

63


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Rubiaceae Aoran<strong>the</strong> penduliflora<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 0.2 1<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 0.3 1<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 0.4 0.5<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 0.7 1<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 0.8 1<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 1 0.75<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 1 0.75<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 1.1 1<br />

Misalai M1 1X40 Forest Rubiaceae Chassalia parvifolia 1.5 1<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Rubiaceae Chassalia parvifolia<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Rubiaceae C<strong>of</strong>fea arabica 4.1 2.5<br />

Kwatango K2 1X40 Forest Rubiaceae Cremaspora sp 0.3 0.5<br />

Kwatango K2 1X40 Forest Rubiaceae Cremaspora sp 1 0.5<br />

Shambangeda S1 5X40 Forest Rubiaceae Gal<strong>in</strong>iera saxifraga 15.5 20<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Rubiaceae Leptact<strong>in</strong>a platyphylla 0.1 0.3<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Rubiaceae Leptact<strong>in</strong>a platyphylla 0.1 0.4<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Rubiaceae Leptact<strong>in</strong>a platyphylla<br />

Pavetta abyss<strong>in</strong>ica var.<br />

0.3 0.5<br />

Shambangeda S1 1X40 Forest Rubiaceae<br />

usambarica<br />

Pavetta abyss<strong>in</strong>ica var.<br />

0.1 0.3<br />

Misalai M1 1X40 Forest Rubiaceae<br />

usambarica<br />

Pavetta abyss<strong>in</strong>ica var.<br />

0.4 1<br />

Misalai M1 1X40 Forest Rubiaceae<br />

usambarica 0.6 1.2<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Polysphaera lanceolata 0.1 0.3<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Polysphaera lanceolata 0.2 0.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Polysphaera lanceolata (3) 0.3 0.4<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Polysphaera lanceolata (5) 0.1 0.4<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Polysphaera lanceolata (5) 0.2 0.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Polysphaera lanceolata (5) 0.3 0.5<br />

Kwatango K2 1X40 Forest Rubiaceae Rothmannia engleriana 0.3 2<br />

Kwatango K2 1X40 Forest Rubiaceae Rothmannia engleriana 1.9 3<br />

Shambangeda S1 1X40 Forest Rubiaceae Rothmannia urcelliformis 0.1 0.75<br />

Misalai M2 5X40 Agr<strong>of</strong>orest Rubiaceae Rothmannia urcelliformis 10 5<br />

64


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M2 5X40 Agr<strong>of</strong>orest Rubiaceae Rothmannia urcelliformis 13.6 5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Rytigynia lichenoxenos 0.1 0.6<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Rytigynia lichenoxenos 0.2 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Rytigynia lichenoxenos (3) 0.1 0.6<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Rubiaceae Rytigynia lichenoxenos (3) 0.2 1<br />

Shambangeda S1 1X40 Forest Rubiaceae Tricalysia pallens 0.5 2<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Rutaceae Citrus s<strong>in</strong>ensis 1.7 1.5<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Rutaceae Citrus s<strong>in</strong>ensis 2.2 1<br />

Shambangeda S1 1X40 Forest Rutaceae Vepris simplicifolia 0.6 1.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sap<strong>in</strong>daceae Allophylus pervillei 0.2 0.6<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sap<strong>in</strong>daceae Allophylus pervillei 0.3 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae Bligia unijugata 1.9 2.5<br />

Kwatango K1 1X40 Agr<strong>of</strong>orest Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 0.2 0.3<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 0.2 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 0.3 0.6<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 0.6 1.5<br />

Kwatango K2 1X40 Forest Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 1.2 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 2.1 1.5<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 2.2 1<br />

Kwatango K2 1X40 Forest Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica 2.3 1<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae De<strong>in</strong>bollia borbonica (2) 0.3 1<br />

Misalai M3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae ( C) Paul<strong>in</strong>ia p<strong>in</strong>nata<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Sap<strong>in</strong>daceae (C ) Paul<strong>in</strong>ia p<strong>in</strong>nata<br />

Shambangeda S1 1X40 Forest Sapotaceae Chrysophyllum gorungosanum 0.1 0.3<br />

Kwatango K2 10X200 Forest Sapotaceae Manilkara sulcata 45 40<br />

Kwatango K2 10X200 Forest Sapotaceae Manilkara sulcata 57 40<br />

Kwatango K2 10X200 Forest Sapotaceae Manilkara sulcata 59 45<br />

Kwatango K2 10X200 Forest Sapotaceae Manilkara sulcata 59.9 40<br />

Shambangeda S1 1X40 Forest Sapotaceae Mimusops obtusifolia 2.3 4<br />

Kwatango K2 1X40 Forest Sapotaceae Pouteria alnifolia 0.1 1<br />

Kwatango K2 1X40 Forest Sapotaceae Pouteria alnifolia 0.2 0.6<br />

Shambangeda S1 1X40 Forest Sapotaceae Sensypelum msolo 0.2 0.5<br />

Shambangeda S1 10X200 Forest Sapotaceae Sensypelum msolo 120 30<br />

65


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Simaroubaceae Harrisonia abyss<strong>in</strong>ica 0.2 1.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Simaroubaceae Harrisonia abyss<strong>in</strong>ica 3.5 2<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Simaroubaceae Harrisonia abyss<strong>in</strong>ica (2) 0.1 0.3<br />

Kwatango K5 1X40 Plantation Simaroubaceae Harrissonia abyss<strong>in</strong>ica 0.1 0.5<br />

Kwatango K5 1X40 Plantation Simaroubaceae Harrissonia abyss<strong>in</strong>ica 0.2 1.5<br />

Shambangeda S1 1X40 Forest Simaroubaceae Quassia undulata 0.1 0.3<br />

Shambangeda S1 1X40 Forest Simaroubaceae Quassia undulata 0.2 1<br />

Misalai M1 1X40 Forest Simaroubaceae Quassia undulata 0.5 0.6<br />

Misalai M1 1X40 Forest Simaroubaceae Quassia undulata 0.5 0.6<br />

Misalai M1 10X200 Forest Simaroubaceae Quassia undulata 30 32<br />

Shambangeda S1 10X200 Forest Simaroubaceae Quassia undulata 39 45<br />

Misalai M1 10X200 Forest Simaroubaceae Quassia undulata 54 50<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Solanaceae ( C) Solanum term<strong>in</strong>ale<br />

Kwatango K2 1X40 Forest Sterculiaceae Cola clavata 0.1 0.3<br />

Kwatango K2 1X40 Forest Sterculiaceae Cola clavata 0.7 2<br />

Kwatango K2 1X40 Forest Sterculiaceae Cola clavata 0.7 2.5<br />

Kwatango K2 1X40 Forest Sterculiaceae Cola clavata 3.3 2.5<br />

Kwatango K2 1X40 Forest Sterculiaceae Cola clavata (6) 0.1 0.3<br />

Kwatango K5 1X40 Plantation Sterculiaceae Dombeya kirkii 2.5 3<br />

Kwatango K5 1X40 Plantation Sterculiaceae Dombeya kirkii 5 3<br />

Kwatango K5 1X40 Plantation Sterculiaceae Dombeya kirkii 5 4<br />

Kwatango K5 1X40 Plantation Sterculiaceae Dombeya kirkii 5 6<br />

Kwatango K5 1X40 Plantation Sterculiaceae Dombeya kirkii 7 4<br />

Kwatango K5 5X40 Plantation Sterculiaceae Dombeya kirkii 10 7<br />

Kwatango K5 5X40 Plantation Sterculiaceae Dombeya kirkii 10 7<br />

Kwatango K4 10X200 Mixed farm<strong>in</strong>g Sterculiaceae Sterculia appendiculata 36 20<br />

Kwatango K4 10X200 Mixed farm<strong>in</strong>g Sterculiaceae Sterculia appendiculata 54 30<br />

Kwatango K4 10X200 Mixed farm<strong>in</strong>g Sterculiaceae Sterculia appendiculata 76 25<br />

Kwatango K5 5X40 Plantation Sterculiaceae Stereospermum kunthianum 24.1 12<br />

Kwatango K5 5X40 Plantation Sterculiaceae Stereospermum kunthianum 26 15<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.7 1.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.2 0.6<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.2 1<br />

66


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.3 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.3 1.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.4 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 0.6 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 1.9 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 2.3 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae 2.5 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae (2) 0.3 0.75<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae (3) 0.2 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae (4) 0.1 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae (5) 0.5 1.5<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Dombeya mupangae (7) 0.4 1<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Sterculiaceae (S) Polysphaera lanceolata 0.1 0.3<br />

Kwatango K5 1X40 Plantation Tiliaceae Carpodiptera africana 0.3 1.5<br />

Kwatango K5 1X40 Plantation Tiliaceae Carpodiptera africana 0.3 2<br />

Kwatango K5 1X40 Plantation Tiliaceae Carpodiptera africana 0.4 2<br />

Kwatango K5 1X40 Plantation Tiliaceae Carpodiptera africana 3 4<br />

Kwatango K5 1X40 Plantation Tiliaceae Carpodiptera africana (2) 2.2 3<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Tiliaceae Grewia forbesii 0.2 0.6<br />

Kwatango K3 1X40 Fallow <strong>land</strong> Tiliaceae Grewia similis 0.1 0.4<br />

Misalai M3 1X40 Fallow <strong>land</strong> Tiliaceae (H) Triumfetta rhomboidea<br />

Misalai M3 1X40 Fallow <strong>land</strong> Tiliaceae (H) Triumfetta rhomboidea<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Tiliaceae (H) Triumfetta rhomboidea (11)<br />

Shambangeda S1 1X40 Forest Ulmaceae Celtis gomphophylla 7.7 10<br />

Shambangeda S1 1X40 Forest Ulmaceae Celtis gomphophylla 9 10<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Umbeliferae Steganotaenia lauraceae 1.9 1<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Umbeliferae Steganotaenia lauraceae 2 3<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Urticaceae (S) Boehmeria macrophylla (19)<br />

Kwatango K4 1X40 Mixed farm<strong>in</strong>g Verbanaceae Premna sp 0.7 1.5<br />

Kwatango K5 5X40 Plantation Verbanaceae Tectona grandis 6 9<br />

67


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Kwatango K5 5X40 Plantation Verbanaceae Tectona grandis 9 7<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Verbanaceae (S) Lantana camara 0.1 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Verbanaceae (S) Lantana camara 0.1 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Verbanaceae (S) Lantana camara 0.1 0.3<br />

Shambangeda S2 1X40 Agr<strong>of</strong>orest Verbanaceae (S) Lantana camara 0.1 0.4<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbanaceae (S) Lantana camara 0.1 1.5<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbanaceae (S) Lantana camara 0.3 1.5<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbanaceae (S) Lantana camara 0.5 1.5<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbanaceae (S) Lantana camara 2 1.5<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbanaceae (S) Lantana camara (2) 0.2 1<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbaneceae (S) Lantana camara (2) 0.1 1<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbaneceae (S) Lantana camara (2) 0.2 1.5<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbaneceae (S) Lantana camara (22)<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbaneceae (S) Lantana camara (4) 0.3 1.5<br />

Misalai M3 1X40 Fallow <strong>land</strong><br />

Monoculture&Mixed<br />

Verbaneceae (S) Lantana camara (8)<br />

Misalai M4 1X40<br />

farm<strong>in</strong>g Verbanaceae (S) Lippia javanica 2 1.5<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbanaceae (S) Lippia javanica (2) 0.2 2<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g<br />

Monoculture&Mixed<br />

Verbanaceae (S) Lippia javanica (3) 0.1 1<br />

Misalai M4 1X40<br />

farm<strong>in</strong>g Verbanaceae (S) Lippia javanica (4) 0.2 1<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Verbaneceae (S) Ro<strong>the</strong>ca myricoides<br />

68


Village<br />

Plot<br />

number<br />

Sub-plot size (m) Land <strong>cover</strong> type<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Verbaneceae (S) Lippia javanica (3)<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.1 0.4<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.1 0.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.1 0.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.2 0.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.2 1<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.3 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.3 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.3 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.4 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.4 1.75<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.5 3<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.6 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.6 2<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.6 2.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.7 2<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 0.8 2<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 1.2 1<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 1.4 1<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 2 2<br />

Kwatango K2 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 2.2 2.5<br />

Kwatango K2 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 2.2 3<br />

Kwatango K2 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia 3.9 4<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (16) 0.1 0.3<br />

Kwatango K2 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (2) 0.2 0.3<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (2) 0.2 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (2) 0.4 2<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (2) 1.3 1<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (3) 0.3 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (3) 0.3 2<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (3) 1.4 1.5<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (5) 0.4 2<br />

69


Plot Sub-plot size (m) Land <strong>cover</strong> type<br />

Village number<br />

Family (Habit) Species DBH (cm) Height (m)<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (6) 0.2 1<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea angustifolia (9) 0.1 1<br />

Shambangeda S1 1X40 Forest Violaceae R<strong>in</strong>orea ferrug<strong>in</strong>ea (2) 0.5 1.5<br />

Misalai M4 1X40<br />

Monoculture&Mixed<br />

farm<strong>in</strong>g Z<strong>in</strong>geberaceae (H) C<strong>in</strong>namom sp (14)<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Z<strong>in</strong>geberaceae (H) C<strong>in</strong>namomum sp (2)<br />

Misalai M2 1X40 Agr<strong>of</strong>orest Z<strong>in</strong>geberaceae (H) Costus sp. (3)<br />

Key for <strong>the</strong> abbreviations: H= herb, S=shrub, C =climber and F=fern.<br />

70


Appendix 3. Transect walks data.<br />

Village Transect Number Distance along transect Coord<strong>in</strong>ates Land <strong>cover</strong><br />

Misalai MT2 0 0460072/9446405 Agr<strong>of</strong>orest<br />

Misalai MT2 50 0460097/9446378 Agr<strong>of</strong>orest<br />

Misalai MT2 100 0460135/9446344 Agr<strong>of</strong>orest<br />

Misalai MT2 150 0460179/9446317 Old fallow<br />

Misalai MT2 200 0460201/9446259 Old fallow<br />

Misalai MT2 250 0460235/9446226 Old fallow<br />

Misalai MT2 300 0460264/9446191 Old fallow<br />

Misalai MT2 350 0460296/9446157 Old fallow<br />

Misalai MT2 400 0460326/9446124 Old fallow<br />

Misalai MT2 450 0460357/9446089 Mixed farm<strong>in</strong>g<br />

Misalai MT2 500 0460392/9446065 Mixed farm<strong>in</strong>g<br />

Misalai MT2 550 0460427/9446065 Monoculture<br />

Misalai MT2 600 0460468/9445999 Old fallow<br />

Misalai MT2 650 0460498/9445969 Mixed farm<strong>in</strong>g<br />

Misalai MT2 700 0460562/9445884 Agr<strong>of</strong>orest<br />

Misalai MT2 750 0460594/9445855 Monoculture<br />

Misalai MT2 800 0460634/9445823 Monoculture<br />

Misalai MT2 850 0460677/9445784 Mixed farm<strong>in</strong>g<br />

Misalai MT2 900 0460717/9445763 Tea field<br />

Misalai MT2 950 0460752/9445735 Monoculture<br />

Misalai MT2 1000 0460782/9445699 Mixed farm<strong>in</strong>g<br />

Misalai MT3 0 Monoculture<br />

Misalai MT3 50 Fallow<br />

Misalai MT3 100 0459696/9444478 Mixed farm<strong>in</strong>g<br />

Misalai MT3 150 0459728/9444442 Monoculture<br />

Misalai MT3 200 0459753/9444402 Mixed farm<strong>in</strong>g<br />

Misalai MT3 250 0459787/9444364 Bush<strong>land</strong><br />

Misalai MT3 300 0459837/9444328 Bush<strong>land</strong><br />

Misalai MT3 350 0459874/9444301 Tea field<br />

Misalai MT3 400 0459896/9444265 Tea field<br />

Misalai MT3 450 0459925/9444230 Tea field<br />

71


Village Transect Number Distance along transect Coord<strong>in</strong>ates Land <strong>cover</strong><br />

Misalai MT3 500 0459959/9444195 Tea field<br />

Misalai MT3 550 0459992/9444158 Tea field<br />

Misalai MT3 600 0460027/9444124 Tea field<br />

Misalai MT3 650 0460050/9444082 Tea field<br />

Misalai MT3 700 0460097/944048 Bush<strong>land</strong>/Tea field<br />

Misalai MT3 750 0460159/9443987 Tea field<br />

Misalai MT3 800 0460202/9443948 Tea/road<br />

Misalai MT3 850 0460276/9443891 Agr<strong>of</strong>orest<br />

Misalai MT3 900 0460304/9443854 Human settlement<br />

Misalai MT3 950 0460356/9443821 Human settlement<br />

Misalai MT3 1000 0460453/9443777 Tea/eucalyptus plantation<br />

Shambangeda S1 0 Agr<strong>of</strong>orest<br />

Shambangeda S1 50 Monoculture<br />

Shambangeda S1 100 Monoculture<br />

Shambangeda S1 150 Monoculture<br />

Shambangeda S1 200 0459387/9440985 Agr<strong>of</strong>orest<br />

Shambangeda S1 250 0459426/9441038 Agr<strong>of</strong>orest<br />

Shambangeda S1 300 0459444/9441080 Old fallow<br />

Shambangeda S1 350 Monoculture<br />

Shambangeda S1 400 0459540/9441153 Monoculture<br />

Shambangeda S1 450 0459576/9441183 Monoculture<br />

Shambangeda S1 500 0459603/9441218 Monoculture<br />

Shambangeda S1 550 0459646/9441257 Monoculture<br />

Shambangeda S1 600 0459680/9441282 Monoculture<br />

Shambangeda S1 650 0459718/9441317 Monoculture<br />

Shambangeda S1 700 0459753/9441344 Monoculture<br />

Shambangeda S1 750 0459791/9441373 Monoculture<br />

Shambangeda S1 800 0459845/9441433 Monoculture<br />

Shambangeda S1 850 0459866/9441436 Agr<strong>of</strong>orest<br />

Shambangeda S1 900 0459905/9441455 Forest<br />

Shambangeda S1 950 0459920/9441494 Forest<br />

Shambangeda S1 1000 0459968/9441518 Forest<br />

Shambangeda S2 0 0458525/9440187 Agr<strong>of</strong>orest<br />

Shambangeda S2 50 0458486/9440210 Monoculture<br />

72


Village Transect Number Distance along transect Coord<strong>in</strong>ates Land <strong>cover</strong><br />

Shambangeda S2 100 0458460/9440250 Old fallow<br />

Shambangeda S2 150 0458409/9440276 Old fallow<br />

Shambangeda S2 200 0458364/9440302 Monoculture<br />

Shambangeda S2 250 0458335/9440313 Monoculture<br />

Shambangeda S2 300 0458291/9440345 Agr<strong>of</strong>orest<br />

Shambangeda S2 350 0458254/9440378 Agr<strong>of</strong>orest<br />

Shambangeda S2 400 0458221/9440409 Monoculture<br />

Shambangeda S2 450 0458196/9440536 Mixed farm<strong>in</strong>g<br />

Shambangeda S2 500 0458167/9440494 Monoculture<br />

Shambangeda S2 550 0458140/9440534 Fallow<br />

Shambangeda S2 600 0458107/9440571 Fallow<br />

Shambangeda S2 650 0458083/9440604 Fallow<br />

Shambangeda S2 700 0458036/9440651 Fallow<br />

Shambangeda S2 750 0458015/9440673 Monoculture<br />

Shambangeda S2 800 0457977/9440704 Monoculture<br />

Shambangeda S2 850 0457938/9440738 Fallow<br />

Shambangeda S2 900 0457908/9440774 Monoculture<br />

Shambangeda S2 950 0457875/9440809 Fallow<br />

Shambangeda S2 1000 Monoculture<br />

Kwatango K1 0 0469314/9447640 Bush<strong>land</strong><br />

Kwatango K1 50 0469729/9446780 Bush<strong>land</strong><br />

Kwatango K1 100 0469725/9446834 Forest<br />

Kwatango K1 150 0469724/9446881 Monoculture<br />

Kwatango K1 200 0469719/9446928 Monoculture<br />

Kwatango K1 250 0469717/9446979 Monoculture<br />

Kwatango K1 300 0469711/9447027 Monoculture<br />

Kwatango K1 350 0469713/9447075 Monoculture<br />

Kwatango K1 400 0469714/9447125 Monoculture<br />

Kwatango K1 450 0469716/9447174 Monoculture<br />

Kwatango K1 500 0469714/9447228 Fallow<br />

Kwatango K1 550 0469716/9447276 Fallow<br />

Kwatango K1 600 0469714/9447328 Fallow<br />

Kwatango K1 650 0469713/9447375 Fallow<br />

Kwatango K1 700 0469717/9447427 Fallow<br />

73


Village Transect Number Distance along transect Coord<strong>in</strong>ates Land <strong>cover</strong><br />

Kwatango K1 750 0469729/9447476 Fallow<br />

Kwatango K1 800 0469722/9447522 Monoculture<br />

Kwatango K1 850 0469720/9447575 Fallow<br />

Kwatango K1 900 0469726/9447626 Monoculture<br />

Kwatango K1 950 0469722/9447677 Bush<strong>land</strong><br />

Kwatango K1 1000 0469718/9447725 Fallow<br />

Kwatango K2 0 0470948/9447456 Old fallow<br />

Kwatango K2 50 0470995/9447457 Old fallow<br />

Kwatango K2 100 0471048/9447455 Old fallow<br />

Kwatango K2 150 0471096/9447458 Fallow<br />

Kwatango K2 200 0471143/9447459 Fallow<br />

Kwatango K2 250 0471193/9447469 Fallow<br />

Kwatango K2 300 Mixed farm<strong>in</strong>g<br />

Kwatango K2 350 0471292/9447480 Monoculture<br />

Kwatango K2 400 0471340/9447482 Fallow<br />

Kwatango K2 450 0471388/9447487 Fallow<br />

Kwatango K2 500 0471440/9447489 Fallow<br />

Kwatango K2 550 0471493/9447488 Fallow<br />

Kwatango K2 600 0471541/9447486 Monoculture<br />

Kwatango K2 650 0471590/9447483 Fallow<br />

Kwatango K2 700 0471644/9447484 Monoculture<br />

Kwatango K2 750 0471689/9447484 Fallow<br />

Kwatango K2 800 0471739/9447474 Fallow<br />

Kwatango K2 850 0471785/9447464 Fallow<br />

Kwatango K2 900 0471839/9447461 Fallow<br />

Kwatango K2 950 0471889/9447460 Fallow<br />

Kwatango K2 1000 0471934/9447465 Fallow<br />

Kwatango K3 0 0471735/9443403 Mixed farm<strong>in</strong>g<br />

Kwatango K3 50 0471732/9443457 Fallow<br />

Kwatango K3 100 0471731/9443500 Bush<strong>land</strong><br />

Kwatango K3 150 0471723/9443549 Bush<strong>land</strong><br />

Kwatango K3 200 0471720/9443602 Bush<strong>land</strong><br />

Kwatango K3 250 0471712/9443651 Fallow<br />

Kwatango K3 300 0471710/9443701 Fallow<br />

74


Village Transect Number Distance along transect Coord<strong>in</strong>ates Land <strong>cover</strong><br />

Kwatango K3 350 0471708/9443749 Fallow<br />

Kwatango K3 400 0471688/9443791 Fallow<br />

Kwatango K3 450 0471677/9443836 Fallow<br />

Kwatango K3 500 0471665/9443882 Monoculture<br />

Kwatango K3 550 0471650/9443934 Bush<strong>land</strong><br />

Kwatango K3 600 0471630/9443981 Bush<strong>land</strong><br />

Kwatango K3 650 0471615/9444026 Bush<strong>land</strong><br />

Kwatango K3 700 0471604/9444071 Fallow<br />

Kwatango K3 750 0471592/9444123 Fallow<br />

Kwatango K3 800 0471576/9444169 Fallow<br />

Kwatango K3 850 0471570/9444216 Bush<strong>land</strong><br />

Kwatango K3 900 0471576/9444267 Bush<strong>land</strong><br />

Kwatango K3 950 Monoculture<br />

Kwatango K3 1000 0471580/9444369 Monoculture<br />

Kwatango K4 0 0471345/9445330 Fallow<br />

Kwatango K4 50 0471315/9445367 Mixed farm<strong>in</strong>g<br />

Kwatango K4 100 0471276/9445398 Monoculture<br />

Kwatango K4 150 0471238/9445431 Monoculture<br />

Kwatango K4 200 0471194/9445446 Monoculture<br />

Kwatango K4 250 0471150/9445468 Fallow<br />

Kwatango K4 300 0471109/9445496 Fallow<br />

Kwatango K4 350 0471071/9445532 Old fallow<br />

Kwatango K4 400 0471025/9445554 Old fallow<br />

Kwatango K4 450 0470981/9445581 Old fallow<br />

Kwatango K4 500 0470940/9445616 Old fallow<br />

Kwatango K4 550 0470903/9445641 Old fallow<br />

Kwatango K4 600 0470864/9445665 Monoculture<br />

Kwatango K4 650 0470824/9445697 Monoculture<br />

Kwatango K4 700 0470782/9445724 Mixed farm<strong>in</strong>g<br />

Kwatango K4 750 0470741/9445755 Monoculture<br />

Kwatango K4 800 0470702/9445785 Monoculture<br />

Kwatango K4 850 0470664/9445814 Fallow<br />

Kwatango K4 900 0470625/9445844 Old fallow<br />

Kwatango K4 950 0470588/9445890 Old fallow<br />

75


Village Transect Number Distance along transect Coord<strong>in</strong>ates Land <strong>cover</strong><br />

Kwatango K4 1000 0470560/9445925 Old fallow<br />

76


Appendix 4. Bird r<strong>in</strong>g<strong>in</strong>g data.<br />

Weight W<strong>in</strong>g Bill Tarsur Tail<br />

Date Village Time Species Age Sex (g) (mm) (mm) (mm) (mm) Remarks<br />

25.10.2008 shambangeda 810 Olive sunbird 9.5 55 30 17 55<br />

25.10.2008 shambangeda 913 Olive sunbird juv 8 57 22 16 42<br />

25.10.2008 shambangeda 1007 Little greenbul 26 83 17 25 80<br />

25.10.2008 shambangeda 748 Yellow streaked greenbul 30 98 22 23 100<br />

25.10.2008 shambangeda 1040 Olive sunbird 10 60 23 19 48<br />

25.10.2008 shambangeda 930 Olive sunbird 9.5 57 25 17 44<br />

25.10.2008 shambangeda 1050 Little greenbul 22 76 12 20<br />

25.10.2008 shambangeda 1120 Olive sunbird 9.5 58 24 17 50<br />

25.10.2008 shambangeda 1125 Little greenbul 29 75 19 15 80<br />

25.10.2008 shambangeda 1240 Olive sunbird 10 60 24 18 86<br />

25.10.2008 shambangeda 1248 Shelley's greenbul 26 80 15 14 78<br />

25.10.2008 shambangeda 1254 Little greenbul 26 76 13 15 80<br />

25.10.2008 shambangeda 1257 Olive sunbird 9 62 25 19 51<br />

25.10.2008 shambangeda 249 Olive sunbird 8.5 51 26 15 46 Blood patch<br />

With down<br />

25.10.2008 shambangeda 250 Little greenbul 24 73 12 18 72 fea<strong>the</strong>rs<br />

25.10.2008 shambangeda 245 Little greenbul 26 83 13 19 78<br />

25.10.2008 shambangeda 302 Forest batis 12 55 15 18 30<br />

25.10.2008 shambangeda 415 Shelley's greenbul 28 80 14 19 73<br />

77<br />

With yellow<br />

gap<br />

25.10.2008 shambangeda 418 Little greenbul 26 81 15 18 72<br />

25.10.2008 shambangeda 425 Little greenbul 27 83 14 17 75<br />

25.10.2008 shambangeda 430 Little greenbul 26 83 13 18 75<br />

25.10.2008 shambangeda 432 Shelley's greenbul Escaped<br />

25.10.2008 shambangeda 441 Shelley's greenbul 31 75 14 19 77<br />

25.10.2008 shambangeda 515 Olive sunbird 9 59 21 17 52<br />

27.10.2008 shambangeda 830 Lttle greenbul 25.5 85 13 19 75<br />

27.10.2008 shambangeda 920 Lttle greenbul 25 86 13 19 77<br />

27.10.2008 shambangeda 1001 Shelley's greenbul 22.5 84 12 19 76<br />

27.10.2008 shambangeda 1220 little greenbul 23 86 14 20 77


Weight W<strong>in</strong>g Bill Tarsur Tail<br />

Date Village Time Species Age Sex (g) (mm) (mm) (mm) (mm) Remarks<br />

27.10.2008 shambangeda 1304 Shelley's greenbul 26.5 82 13 19 76<br />

27.10.2008 shambangeda 1408 Forest batis 11.5 61 12 19 31<br />

27.10.2008 shambangeda 1410 Olive sunbird 9.5 52 22 16 37<br />

27.10.2008 shambangeda 1506 Olive sunbird 7.5 54 22 15 44<br />

27.10.2008 shambangeda 1630 Olive sunbird 9.5 62 22 17 55<br />

27.10.2008 shambangeda 1704 little greenbul 22.5 76 10 20 71<br />

27.10.2008 shambangeda 1720 little greenbul 26.5 87 11 21 78<br />

27.10.2008 shambangeda 1722 white stated forest rob<strong>in</strong> 15.5 77 11 23 57<br />

27.10.2008 shambangeda 1728 white stated forest rob<strong>in</strong> 14.5 75 11 23 55<br />

27.10.2008 shambangeda 1800 little greenbul 24.5 51 12 21 76<br />

27.10.2008 shambangeda 1810 Stripe ckecked greenbul Escaped<br />

28.10.2008 shambangeda 900 white stared forest rob<strong>in</strong> 16 76 12 24 54<br />

28.10.2008 shambangeda 915 yellow seaked greenbul 25 85 17 22 86<br />

28.10.2008 shambangeda 945 yellow seaked greenbul 25.5 87 16 22 87<br />

28.10.2008 shambangeda 1206 white browed rob<strong>in</strong> chat 32 58 15 28 81<br />

28.10.2008 shambangeda 1209 Little greenbul 24 75 12 17 75<br />

28.10.2008 shambangeda 1210 white browed rob<strong>in</strong> chat 40 96 17 33 82<br />

28.10.2008 shambangeda 220 Little greenbul 24 81 12 18 77<br />

28.10.2008 shambangeda 259 shelley's greenbul 26 82 13 20 78<br />

28.10.2008 shambangeda 304 shelley's greenbul 25 79 12 18 74<br />

28.10.2008 shambangeda 420 olive sunbird 8.5 55 22 14 45<br />

28.10.2008 shambangeda 522 peter's tw<strong>in</strong>sport 16 50 14 19 54<br />

28.10.2008 shambangeda 530 Red faced crimsonw<strong>in</strong>g 16 55 15 24 53<br />

28.10.2008 shambangeda 620 olive sunbird 10.5 62 24 17 54<br />

28.10.2008 shambangeda 635 shelley's greenbul 26 80 13 18 78<br />

28.10.2008 shambangeda 636 white stared forest rob<strong>in</strong> 16 72 11 24 55<br />

28.10.2008 shambangeda 638 white stared forest rob<strong>in</strong> 14 75 11 23 57<br />

28.10.2008 shambangeda 639 Little greenbul 23 80 11 21 79<br />

28.10.2008 shambangeda 641 Little greenbul 24 81 12 21 76<br />

28.10.2008 shambangeda 641 olive sunbird 8.5 55 22 18 42<br />

28.10.2008 shambangeda 642 olive sunbird 10 62 22 17 53<br />

78


Weight W<strong>in</strong>g Bill Tarsur Tail<br />

Date Village Time Species Age Sex (g) (mm) (mm) (mm) (mm) Remarks<br />

With yellow<br />

30.10.2008 Kwatango 1130 yellow streaked greenbul juv 34.5 100 25 23 97 gop on <strong>the</strong> bill<br />

With yellow<br />

30.10.2008 Kwatango 1232 yellow streaked greenbul juv 32 82 22 22 90 gop on <strong>the</strong> bill<br />

30.10.2008 Kwatango 133 Black headed weaver m 40 84 22 23 53<br />

30.10.2008 Kwatango 228 peter's tw<strong>in</strong>sport m 9 40 10 12 40<br />

30.10.2008 Kwatango 229 Golden weaver f 25 73 15 20 43<br />

30.10.2008 Kwatango 237 Golden weaver f 24.5 69 16 12 44<br />

30.10.2008 Kwatango 320 Red faced cisticola 14 48 14 23 44<br />

30.10.2008 Kwatango 340 Black headed weaver m 39 83 20 22 50<br />

With breed<strong>in</strong>g<br />

30.10.2008 Kwatango 346 African golden weaver m 25 70 15 23 45 plumage.<br />

With breed<strong>in</strong>g<br />

30.10.2008 Kwatango 348 spectacled weaver f 25 63 17 20 55 plumage<br />

30.10.2008 Kwatango 350 African golden weaver 24 75 23 22 45<br />

30.10.2008 Kwatango 406 Red faced cisticola 16 55 15 24 50<br />

30.10.2008 Kwatango 409 peter's tw<strong>in</strong>sport m 15 50 14 19 54<br />

30.10.2008 Kwatango 500 Red faced cisticola 14 48 14 23 45<br />

30.10.2008 Kwatango 510 Red faced cisticola 14 49 13 22 46<br />

30.10.2008 Kwatango 522 peter's tw<strong>in</strong>sport m 9.5 40 12 11 44<br />

With breed<strong>in</strong>g<br />

30.10.2008 Kwatango 523 African golden weaver m 26 70 15 23 45 plumage<br />

30.10.2008 Kwatango 523 spectacled weaver f 25 63 17 22 56<br />

30.10.2008 Kwatango 530 Red faced cisticola 14 49 13 23 46<br />

30.10.2008 Kwatango 532 Black headed weaver m 41 85 23 26 56<br />

31.10.2008 Kwatango 930 Little greenbul 24 76 13 18 76<br />

31.10.2008 Kwatango 936 white browed rob<strong>in</strong> chat 39 96 17 33 84<br />

31.10.2008 Kwatango 1208 Shelley's greenbul 25 82 14 20 79<br />

31.10.2008 Kwatango 128 Shelley's greenbul 26 78 12 19 75<br />

31.10.2008 Kwatango 130 yellow streked greenbul 35 101 25 23 99<br />

31.10.2008 Kwatango 330 yellow streked greenbul 32.5 86 23 22 98<br />

31.10.2008 Kwatango 408 white starred forest rob<strong>in</strong> 16 73 11 24 56<br />

31.10.2008 Kwatango 520 Olive sunbird 8.5 55 22 18 42<br />

79


Date Village Time Species Age Sex<br />

31.10.2008 Kwatango 530 African gowshak<br />

80<br />

Weight<br />

(g)<br />

W<strong>in</strong>g<br />

(mm)<br />

Bill<br />

(mm)<br />

Tarsur<br />

(mm)<br />

Tail<br />

(mm) Remarks<br />

Escaped from<br />

<strong>the</strong> net.<br />

1.11.2008 Kwatango 900 Forest batis f 12 62 11 21 32<br />

1.11.2008 Kwatango 932 Forest batis m 10.5 60 13 18 34<br />

1.11.2008 Kwatango 1220 African broadbill Escaped<br />

1.11.2008 Kwatango 1240 Yellow streaked greenbul 35 10 25 24 97<br />

1.11.2008 Kwatango 430 Yellow streaked greenbul 33 83 22 22 90<br />

1.11.2008 Kwatango 433 Olive sunbird 8.5 55 22 14 45<br />

1.11.2008 Kwatango 439 Olive sunbird 9 54 23 15<br />

1.11.2008 Kwatango 445 Red faced crimsonw<strong>in</strong>g f 12 56 10 18 43<br />

1.11.2008 Kwatango 520 Shelley's greenbul 26 80 13 18 78<br />

3.11.2008 Misalai 1020 Olive sunbird 9.5 50 27 17 45<br />

3.11.2008 Misalai 1022 Olive sunbird 10.5 45 26 18 49<br />

3.11.2008 Misalai 1130 Shelley's greenbul 27 80 13 19 81<br />

3.11.2008 Misalai 511 Red faced crimsonw<strong>in</strong>g m 12 58 11 19 45<br />

3.11.2008 Misalai 512 Olive sunbird 9 54 24 16 51<br />

3.11.2008 Misalai 515 Yellow streaked greenbul 34 85 24 21 92<br />

3.11.2008 Misalai 530 white starred forest rob<strong>in</strong> 18 75 12 25 57<br />

4.11.2008 Misalai 830 Little greenbul 25.5 86 14 19 76<br />

4.11.2008 Misalai 843 Little greenbul Recaptured<br />

4.11.2008 Misalai 920 Shelley's greenbul 25.5 81 11 24 79<br />

4.11.2008 Misalai 1230 Shelley's greenbul 26.5 84 13 24 80<br />

4.11.2008 Misalai 1248 Olive sunbird 9.5 62 22 17 56<br />

4.11.2008 Misalai 320 Olive sunbird Recaptured<br />

4.11.2008 Misalai 333 Little greenbul Recaptured<br />

4.11.2008 Misalai 340 Red faced cisticola 14 54 16 22 52<br />

4.11.2008 Misalai 508 Red faced cisticola 16 56 17 24 51<br />

4.11.2008 Misalai 517 Peter's tw<strong>in</strong>sport m 15 50 14 20 55<br />

4.11.2008 Misalai 520 Yellow streaked greenbul 35 86 25 22 92<br />

4.11.2008 Misalai 521 Little greenbul 27 89 15 20 75


Weight W<strong>in</strong>g Bill Tarsur Tail<br />

Date Village Time Species Age Sex (g) (mm) (mm) (mm) (mm) Remarks<br />

5.11.2008 Misalai 830 White browed rob<strong>in</strong> chat 33 86 16 29 52<br />

5.11.2008 Misalai 847 Little greenbul 27 87 12 20 81<br />

5.11.2008 Misalai 945 Olive sunbird 10.5 62 25 17 55<br />

5.11.2008 Misalai 1015 Shelley's greenbul 26 80 13 19 79<br />

5.11.2008 Misalai 1130 Olive sunbird 8 53 23 13 39<br />

5.11.2008 Misalai 130 Olive sunbird 8.5 54 22 14 38<br />

81


Appendix 5. Timed species count data.<br />

Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Common bulbul Pycnonotus barbatus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest African citril Turtur tympanistria<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Tambour<strong>in</strong>e dove Stactolaema leucotis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest White- eared barbet Stactolaema leucotis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Silvery-cheeked hornbill Bycanistes brevis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Long-billed Tailobird Apalis moreaui<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Red faced cisticola Cisticola erythrops<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Green barbet Stactolaema olivacea<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Evergreen forest warbler Bradypterus lopezi<br />

15.2.2009 Misalai Agr<strong>of</strong>orest White-browed coucal Centropus superciliosus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Tropical boubou Laniarius aethiopicus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Olive sunbird Nectar<strong>in</strong>ia olivacea<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Common stone chat Saxicola torquata<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Banded green sunbird Anthreptes rubritorques<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Black-fronted bush-shrike Malaconotus nigrifrons<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Black headed apalis Apalis melanocephala<br />

Camaroptera<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Grey-backed camaroptera brachyuran<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Grey cuckoo-shrike Corac<strong>in</strong>a caesia<br />

Phyllastrephus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Yellow-streaked greenbul flavostriatus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Eastern Nicator Nicator gularis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Blue-spotted wood dove<br />

Eastern bronze-naped<br />

Turtur afer<br />

15.2.2009 Misalai Agr<strong>of</strong>orest<br />

pigeon Columba delegorguei<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Klaas's cuckoo Chrysococcyx klaas<br />

Andropadus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Shelley's greenbul<br />

masukuensis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Long-crested eagle Lophaetus occipitalis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest P<strong>in</strong> tailed whydah Vidua macroura<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Fisher's turaco Tauraco fischeri<br />

82


Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Speckled mousebird Colius striatus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Yellow white-eye<br />

Uluguru violet-backed<br />

Zosterops senegalensis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest<br />

sunbird Anthreptes neglectus<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Spectacled weaver Ploceus ocularis<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Trampeter hornbill Bycanistes buc<strong>in</strong>ator<br />

15.2.2009 Misalai Agr<strong>of</strong>orest Cabanis bunt<strong>in</strong>g. Emberiza cabanisi<br />

15.2.2009 Misalai Fallow <strong>land</strong> Common bulbul Pycnonotus barbatus<br />

15.2.2009 Misalai Fallow <strong>land</strong> Purple banded sunbid Nectar<strong>in</strong>ia bifasciata<br />

15.2.2009 Misalai Fallow <strong>land</strong> White-browed rob<strong>in</strong>-chat Cossypha heugl<strong>in</strong>i<br />

15.2.2009 Misalai Fallow <strong>land</strong> Collared sunbird Anthreptes collaris<br />

15.2.2009 Misalai Fallow <strong>land</strong> Tropical boubou Laniarius aethiopicus<br />

15.2.2009 Misalai Fallow <strong>land</strong> Blue-spotted wood dove Turtur afer<br />

15.2.2009 Misalai Fallow <strong>land</strong> Fisher's turaco Tauraco fischeri<br />

15.2.2009 Misalai Fallow <strong>land</strong> Red faced cisticola Cisticola erythrops<br />

15.2.2009 Misalai Fallow <strong>land</strong> Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

15.2.2009 Misalai Fallow <strong>land</strong> African citril Ser<strong>in</strong>us citr<strong>in</strong>elloides<br />

15.2.2009 Misalai Fallow <strong>land</strong> Yellow fronted canary ser<strong>in</strong>us mozambicus<br />

15.2.2009 Misalai Fallow <strong>land</strong> Banded green sunbird Estrilda astrild<br />

15.2.2009 Misalai Fallow <strong>land</strong> Common waxbill Colius striatus<br />

15.2.2009 Misalai Fallow <strong>land</strong> Black and white mank<strong>in</strong> Lonchura bicolor<br />

15.2.2009 Misalai Fallow <strong>land</strong> Cabanis bunt<strong>in</strong>g Emberiza cabanisi<br />

15.2.2009 Misalai Fallow <strong>land</strong> Augur bazzard buteo oreophilus<br />

stephanoaetus<br />

15.2.2009 Misalai Fallow <strong>land</strong> African crowed eagle coronatus<br />

streptopelia<br />

15.2.2009 Misalai Fallow <strong>land</strong> Red eyed dove<br />

semitorquata<br />

15.2.2009 Misalai Fallow <strong>land</strong> Long creasted eagle<br />

Eastern bronze-naped<br />

Lophaetus occipitalis<br />

15.2.2009 Misalai Fallow <strong>land</strong><br />

pigeon Columba delegorguei<br />

15.2.2009 Misalai Fallow <strong>land</strong> Trampeter hornibill Bycanistes buc<strong>in</strong>ator<br />

15.2.2009 Misalai Fallow <strong>land</strong> African green pigeon<br />

Black and white shrike<br />

Treron calva<br />

15.2.2009 Misalai Fallow <strong>land</strong><br />

flaycatcher Bias musicus<br />

15.2.2009 Misalai Fallow <strong>land</strong> Fork tailed drongo Dcruru adsimilis<br />

83


Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Common bulbul Pycnonotus barbatus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Squire tailed drongo Dicrurus ludwigii<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g African citril Turtur tympanistria<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Tambour<strong>in</strong>e dove Stactolaema leucotis<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Tropical boubou Laniarius aethiopicus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Speckled mousebird Colius striatus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Common waxbill Colius striatus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Fisher's turaco Tauraco fischeri<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Banded green sunbird Anthreptes rubritorques<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Yellow fronted canary ser<strong>in</strong>us mozambicus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Olive sunbird Nectar<strong>in</strong>ia olivacea<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Grey headed k<strong>in</strong>gfisher Halcyon leucocephala<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Barred Long-tailed cuckoo Cercococcyx montanus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g African emerald cuckoo Chrysococcyx cupreus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Eastern nicator Nicator gularis<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Common fiscal<br />

Uluguru violet backed<br />

Lanius collaris<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g<br />

sunbird Anthreptes neglectus<br />

Andropadus<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Shelley's greenbul<br />

masukuensis<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Little greenbul Andropadus virens<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Arrow-marked babbler Turdoides jard<strong>in</strong>eii<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Brown-crowned tchagra Tchagra australis<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Blue-spotted wood dove Turtur afer<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g White browed rob<strong>in</strong> chat Cossypha heugl<strong>in</strong>i<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Purple banded sunbid Nectar<strong>in</strong>ia bifasciata<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g Long-crested eagle Lophaetus occipitalis<br />

16.2.2009 Misalai Monoculture&mixed farm<strong>in</strong>g African goshawk Accpiter tachiro<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Collared sunbird Anthreptes collaris<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Olive sunbird Nectar<strong>in</strong>ia olivacea<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Red faced cisticola Cisticola erythrops<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Common waxbill Colius striatus<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Little greenbul Andropadus virens<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest African citril Turtur tympanistria<br />

84


Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Common bulbul Pycnonotus barbatus<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Yellow fronted canary ser<strong>in</strong>us mozambicus<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Black-backed puffback Dryoscopus cubla<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest White-browed coucal Centropus superciliosus<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest African Pygmy k<strong>in</strong>gfisher Ispid<strong>in</strong>a picta<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Long-crested eagle Lophaetus occipitalis<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Fisher's turaco Tauraco fischeri<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Green barbet Stactolaema olivacea<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Silvery-cheeked hornbill Bycanistes brevis<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Trampeter hornbill Bycanistes buc<strong>in</strong>ator<br />

Camaroptera<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Grey backed camaroptera brachyuran<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Dark backed weaver Ploceus bicolor<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Puple banded sunbird Nectar<strong>in</strong>ia bifasciata<br />

17.2.2009 Shambangeda Agr<strong>of</strong>orest Squire tailed drongo Dicrurus ludwigii<br />

Shambangeda Agr<strong>of</strong>orest<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Yellow white eye Zosterops senegalensis<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Tambour<strong>in</strong>e dove Stactolaema leucotis<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Tropical boubou Laniarius aethiopicus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

White-browed coucal Centropus superciliosus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

T<strong>in</strong>y greenbul Phyllastrephus debilis<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

White eared barbet Stactolaema leucotis<br />

18.2.2009 Shambangeda (50%) Blue-spotted wood dove Turtur afer<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Andropadus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Shelley's greenbul<br />

masukuensis<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Banded green sunbird Anthreptes rubritorques<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Evergreen forest warbler Bradypterus lopezi<br />

18.2.2009 Shambangeda (50%)<br />

85<br />

Fisher's turaco Tauraco fischeri


Date Site Land use /vegetation <strong>cover</strong> type<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Species Scientific name<br />

18.2.2009 Shambangeda (50%) Grey cuckoo-shrike Corac<strong>in</strong>a caesia<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Phyllastrephus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Yellow-streaked greenbul flavostriatus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Green-headed oriole Oriolus chlorocephalus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Little greenbul Andropadus virens<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Olive sunbird Nectar<strong>in</strong>ia olivacea<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Common bulbul Pycnonotus barbatus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

White-chested ale<strong>the</strong> Ale<strong>the</strong> fuellerborni<br />

18.2.2009 Shambangeda (50%) Yellow white eye Zosterops senegalensis<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

stephanoaetus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

African crowed eagle coronatus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Green barbet Stactolaema olivacea<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Speckled mousebird Colius striatus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Purple banded sunbid Nectar<strong>in</strong>ia bifasciata<br />

18.2.2009 Shambangeda (50%) Black-bellied starl<strong>in</strong>g Lamprotornis corruscus<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture Sou<strong>the</strong>rn banded snake<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

eagle Circaetus fasciolatus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Long-crested eagle Lophaetus occipitalis<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

African harrier -hawk polyboroides typus<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Little sparrow hawak Andropadus virens<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Black-throated wattle-eye Platysteira peltata<br />

18.2.2009 Shambangeda (50%) Forest batis Batis mixta<br />

86


Date Site Land use /vegetation <strong>cover</strong> type<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Species Scientific name<br />

18.2.2009 Shambangeda (50%)<br />

Fallow <strong>land</strong> (40%) & Agr<strong>of</strong>orest (10%) &Monoculture<br />

Lemon dove Aplopelia larvata<br />

18.2.2009 Shambangeda (50%) Amani sunbird Anthreptes pallidigaster<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Common bulbul Pycnonotus barbatus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Little greenbul Andropadus virens<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Olive sunbird Nectar<strong>in</strong>ia olivacea<br />

19.2.2009 Kwatango Fallow <strong>land</strong> African harrier -hawk polyboroides typus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

streptopelia<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Red eyed dove<br />

Eastern bronze-naped<br />

semitorquata<br />

19.2.2009 Kwatango Fallow <strong>land</strong><br />

pigeon Columba delegorguei<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Black headed weaver Ploceus cucullatus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Crowned hornbill Tockus alboterm<strong>in</strong>atus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Palm -nut vulture Gypohierax angolensis<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Red-tailed ant thrush Neocossyphus rufus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Black-bellied starl<strong>in</strong>g Lamprotornis corruscus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Dark backed weaver Ploceus bicolor<br />

19.2.2009 Kwatango Fallow <strong>land</strong> White-browed coucal Centropus superciliosus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Kenrick's starl<strong>in</strong>g Poeoptera kenricki<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Collared sunbird Anthreptes collaris<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Folk tailed drongo Dcruru adsimilis<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Tropical boubou Laniarius aethiopicus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Speckled mousebird Colius striatus<br />

Camaroptera<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Grey backed camaroptera brachyuran<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Red faced cisticola Cisticola erythrops<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Yellow bishop Euplectes capensis<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Yellowbill Ceuthmochares aereus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> African citril Turtur tympanistria<br />

19.2.2009 Kwatango Fallow <strong>land</strong> African pygmy k<strong>in</strong>gfisher Ispid<strong>in</strong>a lecontei<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Long-crested eagle Lophaetus occipitalis<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Brown -hooded k<strong>in</strong>gfisher Halcyon leucocephala<br />

19.2.2009 Kwatango Fallow <strong>land</strong> P<strong>in</strong> tailed whydah Vidua macroura<br />

87


Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Black-backed puffback Dryoscopus cubla<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Green barbet Stactolaema olivacea<br />

stephanoaetus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> African crowned eagle coronatus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Yellow fronted canary ser<strong>in</strong>us mozambicus<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Fisher's turaco Tauraco fischeri<br />

19.2.2009 Kwatango Fallow <strong>land</strong> Baglafecht weaver Ploceus baglafect<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Red faced cisticola Cisticola erythrops<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Folk tailed drongo Dcruru adsimilis<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Black headed weaver Ploceus cucullatus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Long-crested eagle Lophaetus occipitalis<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Common bulbul Pycnonotus barbatus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Square-tailed drongo Dicrurus ludwigii<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Purple banded sunbid<br />

Eastern bronze-naped<br />

Nectar<strong>in</strong>ia bifasciata<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest<br />

pigeon Columba delegorguei<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Augur bazzard buteo oreophilus<br />

streptopelia<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Red eyed dove<br />

semitorquata<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest White-browed coucal Centropus superciliosus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Dark-backed weaver<br />

African golden weaver<br />

Ploceus bicolor<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest<br />

(yellow weaver) Ploceus subaureus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest White eared barbet Stactolaema leucotis<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest African pygmy k<strong>in</strong>gfisher Ispid<strong>in</strong>a lecontei<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Black-bellied starl<strong>in</strong>g Lamprotornis corruscus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Spectacled weaver Ploceus ocularis<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Crowned hornbill Tockus alboterm<strong>in</strong>atus<br />

Camaroptera<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Grey backed camaroptera brachyuran<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Tropical boubou Laniarius aethiopicus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest African citril Turtur tympanistria<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Yellowbill Ceuthmochares aereus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Yellow white eye Zosterops senegalensis<br />

88


Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Black and white mank<strong>in</strong> Lonchura bicolor<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Tambour<strong>in</strong>e dove Stactolaema leucotis<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Olive sunbird Nectar<strong>in</strong>ia olivacea<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Kenrick's starl<strong>in</strong>g Poeoptera kenricki<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest African emerald cuckoo Chrysococcyx cupreus<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest P<strong>in</strong> tailed whydah Vidua macroura<br />

19.2.2009 Kwatango Agr<strong>of</strong>orest Silvery-cheeked hornbill Bycanistes brevis<br />

streptopelia<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Red eyed dove<br />

semitorquata<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Red faced cisticola Cisticola erythrops<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Common bulbul Pycnonotus barbatus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Crowned hornbill Tockus alboterm<strong>in</strong>atus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Black bellied starl<strong>in</strong>g Lamprotornis corruscus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g White-browed coucal Centropus superciliosus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g P<strong>in</strong> tailed whydah Vidua macroura<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Black-backed puffback Dryoscopus cubla<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Collared sunbird Nectar<strong>in</strong>ia olivacea<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Green barbet Stactolaema olivacea<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Tropical boubou Laniarius aethiopicus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Speckled mousebird Colius striatus<br />

Camaroptera<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Grey backed camaroptera brachyuran<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g African Pygmy k<strong>in</strong>gfisher Ispid<strong>in</strong>a lecontei<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Long-crested eagle Lophaetus occipitalis<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Palm -nut vulture Gypohierax angolensis<br />

stephanoaetus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g African crowed eagle coronatus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g African citril Turtur tympanistria<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Yellow fronted canary ser<strong>in</strong>us mozambicus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Red-tailed ant thrush Neocossyphus rufus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Fisher's turaco. Tauraco fischeri<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Spectacled Weaver Ploceus ocularis<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Yellow Bishop Euplectes capensis<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Helmeted Gu<strong>in</strong>eafowl Numida meleagris<br />

89


Date Site Land use /vegetation <strong>cover</strong> type Species Scientific name<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Common Waxbill Colius striatus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Green Wood hoope Lamprotornis corruscus<br />

20.2.2009 Kwatango Mixed farm<strong>in</strong>g Common Fiscal Lanius collaris<br />

20.2.2009 Kwatango Plantation Tropical boubou Laniarius aethiopicus<br />

20.2.2009 Kwatango Plantation Speckled mousebird Colius striatus<br />

Camaroptera<br />

20.2.2009 Kwatango Plantation Grey backed camaroptera brachyuran<br />

20.2.2009 Kwatango Plantation African Pygmy k<strong>in</strong>gfisher Ispid<strong>in</strong>a lecontei<br />

20.2.2009 Kwatango Plantation Long-crested eagle Lophaetus occipitalis<br />

20.2.2009 Kwatango Plantation Palm -nut vulture Gypohierax angolensis<br />

stephanoaetus<br />

20.2.2009 Kwatango Plantation African crowed eagle coronatus<br />

20.2.2009 Kwatango Plantation P<strong>in</strong> tailed whydah Vidua macroura<br />

20.2.2009 Kwatango Plantation Black-backed puffback Dryoscopus cubla<br />

20.2.2009 Kwatango Plantation Collared sunbird Nectar<strong>in</strong>ia olivacea<br />

20.2.2009 Kwatango Plantation Green barbet Stactolaema olivacea<br />

20.2.2009 Kwatango Plantation Spectacled Weaver Ploceus ocularis<br />

20.2.2009 Kwatango Plantation Yellow Bishop Euplectes capensis<br />

20.2.2009 Kwatango Plantation Helmeted Gu<strong>in</strong>eafowl Numida meleagris<br />

streptopelia<br />

20.2.2009 Kwatango Plantation Red eyed dove<br />

semitorquata<br />

20.2.2009 Kwatango Plantation Red faced cisticola Cisticola erythrops<br />

20.2.2009 Kwatango Plantation Tawny flanked pr<strong>in</strong>ia Pr<strong>in</strong>ia subflava<br />

20.2.2009 Kwatango Plantation Common bulbul Pycnonotus barbatus<br />

20.2.2009 Kwatango Plantation Common bulbul Pycnonotus barbatus<br />

20.2.2009 Kwatango Plantation Common Fiscal Lanius collaris<br />

20.2.2009 Kwatango Plantation Red-tailed ant thrush Neocossyphus rufus<br />

20.2.2009 Kwatango Plantation Klaas's cuckoo Chrysococcyx klaas<br />

20.2.2009 Kwatango Plantation Eastern nicator Nicator gularis<br />

White-tailed crested<br />

Trochocercus<br />

20.2.2009 Kwatango Plantation<br />

flycatcher<br />

albonotatus<br />

20.2.2009 Kwatango Plantation Little swift Apus aff<strong>in</strong>is<br />

90


Appendix 6. Def<strong>in</strong>ition <strong>of</strong> key <strong>land</strong> use <strong>types</strong> used <strong>in</strong> <strong>the</strong> survey<br />

Agr<strong>of</strong>orest – <strong>land</strong> which is hav<strong>in</strong>g mixed crops (subsistence crops (such as maize, oranges etc)<br />

and/or cash crops such as cardamom, c<strong>in</strong>namon etc) plus timber tree species.<br />

Bush<strong>land</strong> – an area <strong>of</strong> predom<strong>in</strong>antly <strong>in</strong>digenous herbs, shrubs and sapl<strong>in</strong>gs, less than 2 m <strong>in</strong> height.<br />

Eucalyptus – commercial plantation <strong>of</strong> Eucalyptus trees.<br />

Fallow – <strong>land</strong> which was previously cultivated and is currently left unattended/without crops for up to 3<br />

years.<br />

Forest – <strong>land</strong> which has been dom<strong>in</strong>ated by <strong>in</strong>digenous trees and <strong>the</strong> <strong>land</strong> should be set aside<br />

purposely for certa<strong>in</strong> activities such as protection or production purposes.<br />

Human settlement – an area predom<strong>in</strong>antly <strong>cover</strong>ed <strong>in</strong> houses, roads, shops <strong>in</strong>clud<strong>in</strong>g <strong>the</strong> cleared<br />

area around <strong>the</strong>m.<br />

Mixed farm<strong>in</strong>g – <strong>land</strong> which is occupied by two or more crops such as maize, cocoyam and<br />

sugarcane.<br />

Monoculture (S<strong>in</strong>gle crop field) – <strong>land</strong> which is dom<strong>in</strong>ated by one type <strong>of</strong> crop such as cassava,<br />

sugarcane, cocoyams etc<br />

Old fallow – as above but for more than 4 years.<br />

Plantation – <strong>land</strong> dom<strong>in</strong>ated by planted timber tree species such as teaks, Eucalyptus, P<strong>in</strong>es etc<br />

Tea estates – <strong>land</strong> which is mostly dom<strong>in</strong>ated by tea fields with scattered forest/tree patches.<br />

Tea field – monoculture <strong>of</strong> tea plants.<br />

Where two <strong>land</strong> <strong>cover</strong> <strong>types</strong> are listed it <strong>in</strong>dicates that <strong>the</strong> plot <strong>in</strong>cludes a proportion <strong>of</strong> both <strong>land</strong><br />

<strong>cover</strong>s.<br />

91

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