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Exploring feasible yields for cassava production for food and fuel in the
context of smallholder farming systems in Alto Molcu,Northern Mozambique
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Exploring feasible yields for cassava production for food and fuel in the context of smallholder
farming systems in Alto Molcu, Northern Mozambique
Sanne van den Dungen
MSc Thesis Plant SciencesPPS 80436
36 credits
June 2010
Supervisors: Ir. Sander de Vries
Dr. Ir. Gerrie van de Ven
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Preface and acknowledgements
From the first contact I had with Ir. Sander de Vries, Dr. Ir, Gerrie van de Ven and Prof. Dr. Ken Giller, Iwas able to express my personal motivations and wishes concerning this thesis. I would especially like to
thank Sander and Gerrie for their patience and support during the length of this thesis. I was able to
shape the research in, what for me was the reason to come to Wageningen: explorative research on
farming systems in Sub-Saharan Africa. I am very happy to have been able to pursue this dream.
There are many people I would like to thank for making the four months of fieldwork research possible,
in Northern Mozambique 2009. First of all I would like to thank Sicco Kolijn for his contaminatingenthusiasm and motivation. I admire his network and am thankful for the help I received in finding a
suitable region for research, for hospitality and concerns. Because of his connections I was able to link
up to World Vision Quelimane under the supervision of Brian Hilton. I thank Brian for his support in
introducing me to the district of Alto Molcu and World Vision staff and thank World vision for all the
support and facilities I received. At World Vision Alto Molcu, I met Sansao Honwana, who has to been
much more than a supervisor to me and providing me with a place to stay and all the support from his
staff I could ask for. Thanks Raol for countless Saturdays picking me up from a weeks work in thevillages even though it was your free day. In Mugema, Nacuaca and Gafaria I thank all the farmers co-
operating in the research and being patient with me. Most of all I am grateful for the insights I was able
to get besides their farming systems: the everyday of life, the stories, the food, traditions and customs.
Antonio, Pedro and Gustodio have been amazingly patient with me during the length of fieldwork,
Trying to answer all my questions and providing me with solid friendship and support. The guest
families: the family of Antonio, Donna Celesta and the family of Xavier I show gratitude to their
hospitality for letting me camp at their premises and joining their meals. I had the honour to have BrunoGolden as my translator in the beginning of the fieldwork. There is absolutely no way of expressing my
appreciation to you. Many times during fieldwork I have thought about how to be able to show to you
what it was like having you to help me I trust you have felt it and I could not have wished for a better
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SummaryCurrently the worlds energy supply system for the 21st century is under intensive debate. Renewable
energy sources, especially biomass, play an important role in the discussion where several scientists
have tried to identify high potential areas for the production of biomass for energy. African countries
such as Mozambique are currently under review, because of a favourable climate, ample land
availability and low population density (Batidzirai et al., 2006). Cassava, a potential crop for the
production of bio-ethanol, is currently being discussed as a feasible option for biofuel production by
smallholder farmers as well as maize and sorghum. However current (cassava) yields are low and
farmers have very limited resources for yield improvement.
This study was developed with the overall goal to explore feasible yields for cassava production for food
and fuel in the context of smallholder farming systems in Alto Molcu, Northern Mozambique with the
objectives of i) assessing the heterogeneity between farms by making a rapid farm characterisation, ii)
estimating current yields of cassava, sorghum and maize of selected smallholder farmers, iii) explaining
current yields of cassava, sorghum and maize, iv) making a yield gap analysis between actual yields from
selected crops from field estimations and feasible potential yields simulated using the FIELD model, v)
collecting parameter input used in the FIELD model.
Three villages (Mugema, Nacuaca and Gafaria) were selected in the district of Alto Molcu to represent
variability at district level. Experts, key-informants, back ground information, and first approach farm
characterisation interviews were used to describe and categorize bio-physical, socio-economic and farm
management practices variability found at village, farm and field level. A farm typology based on expert
knowledge and K-means clustering was developed to analyse variability found at farm level. A dynamic
simulation model FIELD was parameterized with field data, and simulation scenarios were developedfrom the rapid farm characterisation interviews and informal meetings with farmers. The model was run
to study and quantify the cassava yield response of different farm management practices. Due to
circumstances model simulations were only based on soil fertility properties of the sampled fields
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However a large part of the same respondents would use fire for clearing of the field: 59%, 80% and 50%
in Mugema, Nacuaca and Gafaria. The effect of maize residue application on cassava fresh yield was
analysed with the help of the simulation model FIELD. Addition of maize residues had a positive effecton fresh cassava yield with an increase in yield of between 156 237kg/ ha in Nacuaca and 189-449
kg/ha in Gafaria over the three quartiles used per ton maize residue applied.
In general most farmers would only consider the use of manure if they would produce horticultures.
Generally manure was piled up and removed not to be of further use. Simulated yields comparing no
manure and manure application showed an increase of 402-482 kg and 433-1034 kg increase/ ton DM
manure applied for Nacuaca and Gafaria subsequently.
Average yield response per kg applied nutrient was highly variable comparing villages and comparing
quartiles. Increasing levels of potassium was most effective on soils in Nacuaca, while a higher response
(increase kg fresh cassava / kg applied N, P or K ha -1) for phosphorus was found in Gafaria. First and
second quartile classified fields had a lower response and remained at a low yield level compared to the
higher yielding fourth quartile fields. High increase in yield was obtained with NPK fertiliser application
(100:22:83 N:P:K) ranging from 37 to 65 kg yield increase per kg fertiliser added in Gafaria and between
49 and 67 kg yield increase per kg fertiliser added in Nacuaca. Improved fertiliser management was
developed to increase yield response per kg fertiliser applied with the help of available nutrients from
crop residues and manure. An increase in yield of 6, 21, and 35% was attained for 4 th quartile-2nd & 3 rd
quartile and 1st quartile fields for Nacuaca. For Gafaria yield increase due to improved management was
even higher: 22, 34 and 40% yield increase for 4th quartile-2nd & 3rd quartile and 1st quartile fields.
Ranked as the most important crop by 60% and 70% of the respondents in Nacuaca and Gafaria
respectively, cassava plays an important role for farmers in the research villages. Only one third of the
farmers in Gafaria (26%) sold cassava compared to 42% in Nacuaca and 48% in Mugema. Overall cassava
was mostly sold within the community (82% of respondents). When sold cassava was sold as less than
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SUMMARY .................................................................................................................... 5
1.1 Introduction to Mozambique ................................................................................................................... 11
1.2 Agro climatic conditions and land use .................................................................................................... 11
1.3 Poverty and agriculture ........................................................................................................................... 12
1.4 Potential crops for bio fuel: cassava, maize and sorghum ...................................................................... 121.4.1 Reasoning in favour of biofuel production ............................................................................................. 131.4.2 Reasoning against biofuel production .................................................................................................... 14
1.5 Sustainability ........................................................................................................................................... 14
1.6 Introduction to research area ................................................................................................................. 151.6.1 Introduction to Zambzia province .................................................................................................... 151.6.2 Alto Molcu ........................................................................................................................................ 16
1.7 Objectives ................................................................................................................................................. 18
1.8 Theoretical background ........................................................................................................................... 19
1.9 Outline of the thesis ................................................................................................................................. 20
2. MATERIALS AND METHODS ................................................................................. 212.1.1 Introduction to work phases and working steps ..................................................................................... 212.1.2 Study area: Bio-physical and socio-economic description ...................................................................... 23
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2.6 Statistical analysis .................................... ..................................... ...................................... ..................... 30
2.7 Dynamic simulation of crop performance and nutrient balances at field scale .................................... 312.7.1 Model for dynamic simulation at field scale: FIELD ............................................................................. 312.7.2 Developing scenarios .......................................................................................................................... 33
3 RESULTS ................................................................................................................. 35
3.1. Characteristics at village level ................................................................................................................. 35
3.1.1 Village biophysical variability ............................................................................................................... 353.1.2 Socio-economic variability at village level ............................................................................................ 393.1.3 Land use and management practices ...................................................................................................... 47
3.2 Between farm variability ......................................................................................................................... 523.2.1 Short characterisation per farm type ....................................................................................................... 52
4. DYNAMIC SIMULATION OF THE IMPACT OF MANAGEMENT ON CASSAVA
YIELDS ........................................................................................................................ 554.1 Introduction ........................................................................................................................................... 554.1.1 Initial simulated yields: Base run ........................................................................................................... 554.1.2 Nutrient yield response .......................................................................................................................... 59
4.2 Management simulations ......................................................................................................................... 604.2.1 Cassava residues .................................................................................................................................... 604.2.2 Maize residue ........................................................................................................................................ 62
4.2.3 Manure application ................................................................................................................................ 634.2.4 Fertiliser use .......................................................................................................................................... 654.2.5 Cost benefit analysis of fertiliser use ...................................................................................................... 654 2 5 Cost benefit analysis of fertiliser use 66
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5. DISCUSSION .......................................................................................................... 73
5.1. Evaluating the effect of farm management on cassava yield .................................................................. 735.1.1 Incorporation of crop residues ............................................................................................................... 735.1.2 Manure application ................................................................................................................................ 745.1.3 Use of fertiliser ...................................................................................................................................... 745.1.4 Feasibility of yield increase scenarios .................................................................................................... 765.1.5 Model FIELD considerations ................................................................................................................. 77
5.2 Evaluation of feasibility .......................................................................................................................... 785.2. 1 Potential crops for biofuel; cassava, maize and sorghum .................................................................... 78
5.3.Methological considerations ........................................................................................................................... 805.3.1 The use of a farm typology .................................................................................................................... 805.3.2 Yield estimations ................................................................................................................................... 815.3.3 Limitations of research .......................................................................................................................... 81
6. CONCLUSIONS ................................................................................................. 83
REFERENCES ............................................................................................................ 85
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APPENDIX I: ADDITIONAL BACKGROUND INFORMATION .................................... 88
APPENDIX II: SOIL FERTILITY ANALYSIS ............................................................... 89
APPENDIX III: SOCIO-ECONOMIC ANALYSIS ......................................................... 91
APPENDIX IV: FARMERS ESTIMATIONS AND QUEFTS MAIZE YIELD
ESTIMATIONS ............................................................................................................ 94
APPENDIX IV (CONT): CASSAVA AND SORGHUM YIELD ESTIMATIONS ............ 95
APPENDIX V: FARM TYPOLOGY .............................................................................. 96
APPENDIX VI: MODEL ASSUMPTIONS .................................................................... 98
APPENDIX VII: FIELD SIZE CASSAVA AND MAIZE ................................................. 99
APPENDIX VIII: CASSAVA AND MAIZE YIELD ESTIMATIONS .............................. 100
APPENDIX IX: FARM TYPOLOGY CONSIDERATIONS .......................................... 103
APPENDIX X: QUARTILE CONSIDERATIONS ........................................................ 104
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1 Introduction
1.1 Introduction to MozambiqueMozambique is located in southern Africa and has around 80 Mha of land and a coastline of 2500 km, a
population density of 22/km2 and approximately 19 million inhabitants. Projections estimate an increase
to 28 million inhabitants by the year 2025 (Batidzirai et al., 2006). Mozambique has been reported as
one of the poorest countries despite the high economic growth
during the 1990s and has only recently been recovering from 16
years of devastating civil war and resulting famine (Bias and
Donovan, 2003 ; Maria and Yost, 2006). An estimated 80% ofMozambican labour is currently used in agriculture; productivity
however is low as agriculture only contributes up to of the GDP
(Bias and Donovan, 2003). According to Wils (2002) three macro-
socio-ecological zones can be defined in Mozambique: The Northern
region (Niassa, Cabo Delgado and Nampula), The Central region
(Zambzia, Tete, Manica and Sofala) and the Southern region
(Inhambane, Gaza and Maputo, see Figure 1). The Northern region
covers around 50% of the total land area and is inhabited by 33% of
the population. The Central region consists out of 29% of the total
land area with 41% of the Mozambican population. Finally the
Southern region forms 21% of the total land area and provides a
home for 26% of the population. These regions were derived based
on the existing administrative, demographic and hydrologic characteristics of the country.
1.2 Agro climatic conditions and land useThe county exhibits great diversity in geological and climatic diversity: from low lying coastal plains
( 200 ) h id i l i i ( 1000 ) d i f ll i f 00 i h
Figuur 1. Overview of Mozambique's
provinces
Figure 1. Overview of Mozambique's
provinces
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1.3 Poverty and agriculture
In 2000, 70% of the Mozambican population lived below the poverty line (UNDP, 2000). Around three
million families are farming in the rural area and obtain 70% of their food from their own on-farm
production (MAM and MEM, 2008). Interestingly enough the poor and the less poor (classification used
by Bias and Donovan, 2003) have approximately the same amount of land per household (each plot of
land is called a machamba). The differences however lie in the amount and the type of input the poor
and less poor can use on their land. For example the amount of land irrigated is higher for the less poor.
Furthermore questionnaires (MINAG, 2007) show that only 4% of the farmers use fertiliser; generally,
the amount of inputs used in Mozambique is very low which is reflected in low crop yields. The low
usage of inputs such as improved seed, fertiliser and technology is mainly due to limited capital,
mechanization and poor access to financial support for the farmers. The Mozambique Biofuel
Assessment (MAM and MEM, 2008) concludes that the amount of land is not a limiting factor for poor
peasants, but rather the capacity to work the land. The average maize yield for Mozambique is
approximately 0.9 tons/ha, which is the lowest yield in Southern Africa: Malawi (1.7 tons/ha), South
Africa (2.8 tons/ha), Swaziland (1.5 tons/ha), Tanzania (1.2 tons/ha), Zambia (1.5 tons/ha) and
Zimbabwe with 1.5 tons/ha (FAO, 2005). Compared to the global average of 4.5 tons/ha these averages
are low, in European countries the production is overall higher and records exist of 15 tons/ha (MAM
and MEM, 2008).
Mozambican agriculture can be characterized by a large number of small-scale producers that have to
rely on rain fed production systems for their subsistence farming. Most important crops grown by small
holder farmers in Mozambique are (in order of importance): maize, cassava, cowpeas, groundnuts,
sorghum, rice, bambara beans/nuts, pigeonpeas , sweet potato, common beans, and millet (Bias andDonovan, 2003). Maize, cassava and sorghum are grown by 79%, 63% and 27% of the of small holder
farm households with a national production of 150, 755 and 34 metric tons subsequently (Bias and
2003 I G 200 ) i d h b h d
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Sorghum provides the staple food of many of the worlds poorest and most food insecure people in the
semi-arid tropics of the world. Because of its genetics sorghum is able to grow in hot and dry agro-
ecological zones where it would be difficult to grow other food grain crops. Sorghum can produce grainsand stover in areas with frequent droughts (Borikar et al., 2007). Sweet sorghum (Sorghum bicolor L.
Moench) is similar to grain sorghum in appearance and agronomic performance. Because of its C4metabolism sorghum is photosynthetically efficient. Like sorghum, sweet sorghum can be cultivated
over a wide range of environments; the difference between the two is that sweet sorghum stores much
of its photosynthates as sugar in the stalks. However sweet sorghum also produces reasonable grain
yields. According to Reddy (2007) sweet sorghum could be grown on the 23.4 million hectares of dry
land in Africa (55% of global sorghum area) where it could produce more biomass and grain if yield-enhancing technologies would be stimulated by the bio fuel market.
Maize is produced almost throughout the country, however most of the production (70%) is
concentrated in the central region and in the north (MINAG, 2007). As sorghum, maize is a C4 crop
which under semi arid ecological conditions is favourable.
Government permission for using these three crops for biofuels is currently heavily debated in
Mozambique. However, in the scope of explorative research they will still be considered in this research,
but the main focus will be on cassava.
1.4.1 Reasoning in favour of biofuel production
Currently the worlds energy supply system for the 21st century is under intensive debate. Renewable
energy sources, especially biomass, play an important role in the discussion where several scientists
have tried to identify high potential areas for the production of biomass for energy. African countries
such as Mozambique are currently under review (Batidzirai et al., 2006). Large scale biomass conversionto for example ethanol could offer a sustainable alternative for part of the current African fuel
consumption or provide export opportunities. Scenario studies estimate biomass production potential
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1.4.2 Reasoning against biofuel production
In large parts of the country maize, cassava and sorghum are considered as staple food hence using
these crops for ethanol production could jeopardize food security. From surveys held in 96/97 it wasconcluded that a large amount of farmers growing the primary crops mentioned above were not able to
sell them: both in rural areas as for the urban poor with agricultural land. Cassava was grown
throughout the country but rarely sold (Bias and Donovan, 2003). Prices of those crops could rise and
availability could be limited creating problems for those without land or insufficient production. Local
processing mills that transfer maize into meal for household consumption using raw material could be
put into problems by the demand for maize for ethanol (MAM and MEM, 2008). However if production
would increase, maize could be considered for ethanol production, especially in certain parts of thenorth and the south where sorghum accounts for a larger part of peoples diet. It will be important to
include the impact of a diet crop being used for ethanol in that dietary region on household food
expenditure in the modelling since this is lacking in previous studies. For all crops investigated (maize,
cassava and sorghum) household consumption and surplus for the market therefore needs to be
identified. One of the main biophysical problems in the production of the crops mentioned above is soil
fertility.
1.5 Sustainability
Since its introduction in 1987 by the Brundtland Commission the concept of sustainability has been of
increasing importance in science, policy formulation and practice. In the Brundtland report sustainability
has been defined as meeting the needs of the present generation without compromising the ability of
future generations to meet their needs (Brundtland, 1987). However since the introduction of the
concept more than 300 different definitions have been developed. A shared characteristic amongst
these is the notion that sustainability is aimed at improving both the current and the future quality oflive. In the scope of scenario studies for biofuel production for the future, sustainability of farming
systems is a key factor. Sustainable agriculture is a form of agriculture concerned about the ability of an
t t i d ti i th l t S t i bl i lt h th j t
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1.6 Introduction to research area
Zambzia province was selected as an interesting province for conducting the research. Below the
province and selected district will be further discussed, in section 2.1 the selection of the villages within
Alto Molcu district will be explained.
1.6.1 Introduction to Zambzia province
Zambzia province produces more than one quarter of the countries cassava, about 18% of the total
maize production and 15% of the countrys total sorghum production and this share remains stable over
the years (Bias and Donovan, 2003; MAM and MEM, 2008). In total Mozambiques area covers 79 mln
hectares of which 12% is arable land suitable for cropping (MAM and MEM, 2008). Zambzia provinceoccupies 105.000 km2 of land with 27.500 km2 suitable for arable production of which 23% is cropped
with cassava, 37% with maize and 5% with sorghum (Statoids, 2007). Other crops grown are pigeonpea
and rice (Table A 1 in the Appendix). Around 26% of the area of Zambzia province is suitable for arable
production, which is the highest percentage compared to other provinces such as Nampula (24%)
Maputo (17%) and Inhambane (14%) (MAM and MEM, 2008).
The highest yields per ha for cassava in Mozambique have been recorded in Zambzia and Nampula
province (Bias and Donovan, 2003). Average production ranges from 6.4 t/ha in Southern Province Gaza
to about 9.0 and 10 ton/ha in more Northern Provinces Zambzia and Nampula respectively (Table 1).
High yield losses ranging from 21-33% are mainly due to prevalence of diseases and plagues such as
cassava brown streak, cassava mosaic virus and termites. Sorghum yield data are unavailable but
estimated around 0.3-0.6 t/ha with a potential between 0.8 and 2 t/ha. For maize a range of 0.4-1.3 t/ha
and an estimated potential of 5-6 t/ha is estimated by the Ministry of Agriculture and Fisheries (MAP,
1997).
Table 1. Yields of fresh cassava (t/ha) per Province (IITA, 2003)
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1.6.2 Alto Molcu
Alto Molcu district is one of the largest districts of Zambzia province and covers an area of 6.386 km2
which equals 6% (DRAM, 2007; Molcu, 2008). Located in the north of the province in between
Quelimane in the south (circa 400km) and Nampula in the north (219km) at national road number one,
latitude 1615 O and longitude 3715 W). The district borders in the north with the river Ligonha, which
separates Zambzia from Nampula province, in the south by the district of Ile, in the west by the district
of Guru and in the east by the district of Gile (Figure 2).
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The district of Alto Molcu is characterized by its mountains (900m) in the west in the direction of Ile
and Guru, its plains (200-300m) in the south and centre and low riverbeds of the main river Molcu
that explain the name of the district (alto = high in Portuguese). Different crops can be grown accordingto the variation in elevation. Along the rivers: rice, coconut, sugarcane, tubers, fruits and vegetables and
grassland. The plains make up 2/3 of the districts surface undulating gradually in the direction of the
mountainous zones. Primary crops grown here: maize, sorghum, beans, sunflower, cotton, sesame,
sweet potato, cassava, fruits, cashew, tobacco and horticultures as well as grass for cattle. The
mountainous zone is cropped with: coffee, maize, sorghum, Irish potato, sweet potato, beans, sesame,
soy, cassava and fruits. Because of its differences in elevation two climatic zones can be identified:
tropical humid (90-100% humidity) and a tropical mountainous climate. Average yearly temperaturevaries between the plains and the mountainous area around 26C and 20C respectively. Two seasons
can be identified in the two climatic zones present in the district: the hot and rainy season from October
till April and the dry and fresh season from Mai until September. Yearly rainfall varies between 1000 mm
on the plains and 1300 mm in the mountains and is distributed in a uni modal pattern with peaks from
December to March (Figure 3)(DRAM, 2007).
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1.7 Objectives
The overall goal of this work was to explore feasible yields for cassava production for food and fuel in
the context of smallholder farming systems in Alto Molcu, Northern Mozambique. This was done by
meeting with the following objectives in three phases.
Phase I objective was aimed at a concise literature study to provide with agronomic background
information on Mozambique and to explore the debate about potentials and drawbacks of biofuel
potential. The second phase was aimed at providing with information and insights from field work. The
third phase needed the input of the first and second phase for scenario development.
Phase I
- To make an exploration in literature to give agronomic background information in Mozambique
and to explore the biofuel debate in Mozambique
Phase II
- To asses heterogeneity between farms by making a rapid farm characterisation
- To estimate current yields of cassava and sorghum of selected smallholder farmers
- To explain current yields of cassava and sorghum of selected smallholder farmers in relation to
soil, landscape and management variability
- To collect parameter input to be used in model FIELD
Phase III
- To make a yield gap analysis between actual yields from field research and feasible yields
simulated using model FIELD
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1.8 Theoretical background
The methodological approach followed in this thesis assumes that the sources of variability found atdifferent levels and scales are nested within each other: the smaller scale (e.g. field) variability
contributes to variability at larger scale (farm or village). Figure 4 illustrates how in a given region
comparisons can be made at village level: capturing average farm and field characteristics and
comparing between study villages, a step further downscaling farms can be compared using a developed
typology of farms within and between villages. Subsequently fields can be compared between
typologies and between villages.
Figure 4. Illustration of conceptual approach of variability at different levels in the research (for an n amount of
fields, farms and villages in a given region), arrows indicate comparisons between components
F t l
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The positivist method followed as the second step in which the output of the rapid farm
characterisation formed the basis of designing a typology.
1.9 Outline of the thesisThe Sections 1.1 to 1.6 have provided the background information on Mozambique and the biofuel
debate. This is used as a starting point for the rest of the thesis. Chapter 2 introduces the methodology
used during the different phases and working steps and explains in several subchapters at which level
analysis are done. Chapter 3 is divided into three parts aimed at describing farm heterogeneity at
different scales of analysis. Part 1 (Section 3.1) analyses results found at village level: comparing
between villages in terms of soil fertility, socio-economic characteristics, production activities and
managerial aspects. Part 2 (Section 3.2) focuses on analyzing differences found comparing within
villages based on the designed typology. Subsequently Chapter 4 presents the results of FIELD model
simulations on cassava crop yields under different farm management scenarios. Chapter 5 is used for a
general discussion and Chapter 6 for concluding remarks and recommendations. Each chapter gives a
brief introduction about its contents and when indicated also a short summary at the end to make some
important concluding remarks to facilitate interpretation of the chapters. Many tables can be found in
the Appendices; within the main text explicit reference to the appendix is made.
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2. Materials and methods
2.1.1 Introduction to work phases and working steps
Three work phases and four main working steps can be identified in this thesis to cope with the
variability found at different scales and to comply with the multiple objectives presented earlier
(Chapter 1.7). Figure 5 below gives a schematic overview of the work phases, working steps and the
interactions between the different components.
The first phase (Phase I) consisted of an elaborate literature review to provide a solid background for the
start of fieldwork. It provided necessary knowledge on the methods needed in the following steps of the
research such as the design of a questionnaire for the rapid farm characterisation and how to develop a
farm typology.
The second phase was aimed at field work and analysis of the data collected. Each step used a previous
step for input and provided information for the following one (Figure 5) For example previous to Step 1
experts were consulted and introduction visits to the area were made that provided the input needed to
start the rapid farm characterisation in the 3 villages. With the help of key informants, 25 farmers ineach village were chosen (74 in total, one missing). Socio-economic and managerial data was collected
as well as farmers yield estimations. The first approach questionnaire was used for this step (Appendix
A 23). The output of Step 1 served as a basis for Step 2: the typology. After development of this farm
typology selected farmers (a subset of 10 per village) was revisited for a second and third round of
questionnaires to cross-check and validate previous data and answers. During these second and third
visits soil samples were taken and area and harvest measurements for the crops of focus were done. As
a third step results were analysed at multiple scales for the villages, farms and fields (Figure 4).
Phase III continues at the end of step 3 from phase II: the analysis provided a framework for feasible
i f i d t b f fi ld d f l l M i ki t 4 i h III
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2.1.2 Study area: Bio-physical and socio-economic description
The district of Alto Molcu was chosen before arrival in collaboration with the locally, nationally and
internationally active aid organization World Vision and agricultural experts of the region. Upon arrivalin the area in the end of April 2009, key informants (extension officers, researchers and NGOs) were
contacted in the district of Alto Molcu. After several meetings in which the objectives were explained
to those key informants three potential research villages were selected. Study sites with different soil
types, different importance of cassava in the farming system and different distance to the markets were
selected. The procedure was facilitated using a Global Position System (GPS) device to record GPS
coordinates and a GIS soil map (Appendix A24) of the district to cross check for soil type variability
between the sites. Main characteristics of the selected study sites are listed below in Table 2.
Mugema Nacuaca Gafaria
BiophysicalAltitude (masl) 610 711 710
Dominant soil types (FAO) Ferric Acrisol (sandy) Cambio Arenosol Ferric Acrisol (loamy)
Description soil type low levels of plant nutrients,
excess aluminium, and high
erodibility,
a fine-textured subsurface layer,
low water and nutrient holding
capacity
low levels of plant
nutrients, excess
aluminium high
erodibility, high
contents ofkaoliniticclay and iron and
aluminium oxides,
Landscape Plains slightly undulating rivers Plains slightly undulating Hilly surroundings
Table 2. Some biophysical and socio-economic characteristics of the selected villages (IIAM, 1996; Report, 2007; unknown,
2007)
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Initially it was the intention to use the three selected villages Mugema, Nacuaca and Gafaria for all three
survey rounds, soil samples and harvest estimations. Unfortunately due to unforeseen circumstances
and limitations in time Mugema was only visited for the rapid farm characterisation. This made inclusionof Mugema for purpose of designing a farm typology possible, but further analysis on soil samples and
harvest estimations not possible. Result from the rapid farm characterisation in Mugema will therefore
only be used in the first part of Chapter 3: the analysis on village level (Section 3.1.2) and in the chapter
on farm typology (Section 3.2).
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2.2 Farm sampling and characterisation
2.2.1 Rapid farm characterisationAfter the introduction and site selection local leaders in the villages were consulted about the possibility
and approval for carrying out the survey. In all three villages permission was obtained and a suitable key
informant per village was selected. The key informant then helped to select 25 households per village,
with contrasting household characteristics according to his knowledge. Special attention was paid to
avoid sampling bias by taken extra notice of the spatial distribution of selected farmers over the area of
study. Age distribution, ratio male: female respondents and NGO involvement of interviewees was taken
into account. Consequently surveys for the rapid farm characterisation were designed to capture bio-physical, socio-economic and managerial aspects of each selected farm and questions were checked
through triangulation. Emphasis was placed on quantifying yields, sales and the use of inputs such as
animal manure and hired labour and to explore the farming system in general. Overall the survey was
aimed at characterisation of typical smallholder farm in term of size, composition, production systems,
agricultural practices, labour and land with a focus on cassava, sorghum and maize. A mixture of
structured and un-structured questions was used and carried out by the author, a translator and the key
informant, which allowed for further questioning if answers given were unclear or not correspondingwith observations. The questionnaire is given in Appendix Table A 23.
2.2.2 Farm typology
After the first round of questionnaires (May- June 2009) obtained data was processed using statistical
software (SPSS 17.0) and Excel. Relationships between important variables on crop yield, crop
management, socio-economics, farming system and animal husbandry were explored using Pearson
bivariate correlations. Data from the rapid farm characterisation was analysed and farm household
typologies were constructed using the following multivariate statistical techniques as proxies for
categorization; Principal Component Analysis (PCA) and Cluster Analysis (CA) and were combined with
expert knowledge and preliminary household characterisation during fieldwork. PCA can be defined as a
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preliminary characterisation with help of experts and exploration of field data was used to compare
different cluster outputs and to choose the most appropriate one.
2.2.3 Second and third round interviews
A subset of 2 farmers per typology (of the initially proposed typology) per village were chosen. The initial
first made typology was based on dividing the farmers according to farm income, farm involvement and
several wealth indicators suggested by experts. This approach will be discussed in Chapter 5.3.1 further
in this thesis. Later the used typology was revised, but the first typology made during fieldwork was used
for the selection of second and third round questionnaires. Besides asking for further details on crop
and soil fertility management, marketing and pest & diseases, the second round of questionnaires was
used to cross-check important information from the first round. For this second part of surveys fields of
cassava, sorghum, maize and fallow fields were visited together with the farmer. During the first round
of questionnaires and visits to farmers it was observed that what is called a machamba (field) by
farmers, is upon a closer look quite heterogeneous and could be divided in more homogenous sub-
machambas. A cassava field was considered as such if it would have the same characteristics for: i) time
of planting (in months), ii) ridges or heaps and iii) use of mixed cropping. For sorghum and maize only
the use of intercrop was used to identify a sub-field. Since farmers would fallow only a subplot of the
whole field, only the part used in the next cropping season was measured and recorded in the survey.
After defining the area was calculated using a differential GPS. Subsequently, the areas were plotted as
polygon in ArcGIS software in GIS soil layers.
2.3 Field biophysical characterisation
2.3.1 Soil sampling and analysis
For the cassava fields separate samples were collected from rows and from ridges/hills. Together withfarmers a distance of 20 cm from the stem was chosen for sampling in ridges/hills to avoid damaging the
tubers. To avoid oversampling the same number of soil samples in the ridges/hills as in between the
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2.3.2 Field measurements
Bio-physical information per field was collected and included e.g. visible signs of erosion,
characterisation of surrounding fields (cultivated or fallow), and management: e.g. crop rotation, mixedcropping, history of cultivation, labour, weeding and handling of crop residues.
Distance in beds, distance between rows and height at 10 randomly chosen plants in each identified
cassava field were measured and recorded. A weed management score from 1 (very poor) to 5 (very
good) was used to quantify presence of weeds and subsequently weed management of the farmer.
Plant density (plants m-1) and plant population (PP, plants ha -1) were estimated by considering the
average over at least 5 distances between rows (BR, in meters) and between plants spacing (BP, in
meters) to calculate the expected plant population according to following equation:
Pl. density (plants m-2) = 1 / (BR x BP)
Because non productive stalks were replaced with productive stalks a correction factor for crop survival
was not included. This means that for estimation of plant population (PP, plants ha -1) the assumption
was made that all individual plants are productive and at least 5 measuring points between rows and
between plants are representative for plant density in each individual field.
2.4 Yield estimations
Yield estimations of several crops produced by the farmers in the villages were estimated using the
following different approaches:
farmers estimates of household production (per crop produced in ton per household)
farmers estimates of crop production per individual field (for cassava, sorghum and maize fieldsin t/ha)
calculations from harvest estimations in the field (only for cassava in t/ha)
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Farmers estimating crop yield per individual field
During the three rounds of farm visits farmers were asked to estimate cassava harvest (kg dried
cassava), maize and sorghum per field visited. Only for cassava a conversion from dried to kg freshweight tubers using 33% DM as a rule of thumb was used (Fermont et al., 2009).
Calculations estimating cassava yield from harvest measurements in the field
In consensus with the farmer, a number of plants were selected for harvest by the researcher. The
individual plants were specifically chosen to represent average plants present in each field. Farmers
helped in finding representative plants by clearing the soil around the cassava plant and judging its
representative characteristics by tuber size and amount of tubers. Selected plants were uprooted, soil
removed and weighed as a whole. Next tubers were removed and weighed in total, subsequently
marketable tubers were selected and weighed. Tubers were considered marketable if > 3cm in
diameter, damage and disease free. Name of cultivar was recorded together with the notation bitter or
sweet. Fresh tuber weight (IFW in kg plant-1) could then be calculated out of the average of measured 5
individual plant tuber weights corrected for months after planting (MAP) and set on a standard of 12
months. Total fresh tuber weight (TFW in t ha -1) was calculated using following equation:
TFW (t ha-1)=IFW (kg plant-1) x Plant population (PP, in plants ha-1)
Calculations estimating sorghum yield from harvest estimations in the storage facility
In the research area sorghum is harvested in between June and July. Initially the objective was to be part
of the harvest of sorghum in order to make harvest measurements. Because not all farmers were able to
estimate the amount of sorghum harvested (usually referred to as heap and store) an alternative had
to be found. Sorghum throughout the research area is stored in an identical way: the whole panicle is
piled up in a heap of panicles. The size of the storage of sorghum of farmers revisited was measured and
adjusted to geometrical shapes. For these shapes size in m3 was calculated. From a subset of farmers a
few panicles were collected. These were weighed as full panicle and volumetric (m3) size of the panicle
estimated using a beaker filled with water After drying the harvest index of the panicle (HI ) was
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2.5 Income calculations
2.5.1 Household income calculationsA distinction in sources of income was made following the assumption that total estimated farm income
is the sum of income from crops, income from selling animals and animal products and off farm sources
of income as listed below:
Total estimated farm income = Income from crops + Income from animals + Off farm income (other
sources of income)
Income from crop productionGross value per crop or crop product (GVC) per household was estimated by multiplying fresh weight
(FW) of the product by the average selling price. Average selling prices and estimated fresh weights
were collected during the three farm visits. The sum of all GVC subsequently formed total income from
crop production in New Mozambican Meticals (MZN).
Income from animal production
Gross value from animal production (GVA) per household was estimated by multiplying the number of
animal type sold times average selling price. A summation of GVAs per animal type plus the value of
animal products sold formed the income from total animal production (GVAT).
Off farm income
During the interviews farmers were asked for involvement in off farm activities such as making blocks,
sieves or stoves, having a contract job (e.g. driver or teacher) and receiving pensions and remittances on
a yearly basis. The sum of all activities belonging to non-farm sources of income is off farm income.
2.5.2 Gross margin fertilizer analysis
Partial gross margins of NPK fertiliser for simulated yields were calculated for a total of 90 individual
fields in both Nacuaca and Gafaria Average wholesale market prices for 2009 were used for the full
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2.6 Statistical analysis
Analysis of socio-economic diversity
Comparisons across sites and farm typologies in terms of socio-economic indicators, land use and
managerial variables were done through calculation of descriptive statistics and analysis of variance.
This analysis was done with the explanatory factors Village and Typology and their interaction, and
means were compared with the 5% LSD or 10% LSD if indicated. A principal component analysis (PCA)
was conducted using the socio-economic data (previous log or square root transformed and
standardized for comparable ranges) to identify important proxy indicators further used in the
development of the typology. Due to the experimental design of three villages and four farm types in a
non-equal distribution the ANOVAs were conducted under the unbalanced treatment structure of
offered in SPSS (17.0) under Univariate Generalized Mixed Models.
Soil fertility variability
Soil fertility status was assessed at village, farm and field level through calculation of descriptive
statistics and analysis of variance with Village or Quartile as explanatory factors. This analysis was done
based on soil properties pertaining to individual fields (N=90) expressed as results from chemical
analysis of soil organic C, total N (%), available P, exchangeable K, Ca and Mg, pH, CEC, sand (%), silt (%)
and clay (%) contents in a composite sample per field. The model FIELD was used to divide fields
according to their yields in four significantly different quartiles, to cope with variability within villages.
Explaining simulated yield variability
To be able to identify variables best explaining yield differences a multiple linear regression was carried
out. As a first step variables were checked for correlation using Spearmans and Pearsons correlation
analyses. For any pair of abiotic, biotic and management variables with inter-correlations (r) greaterthan 0.7 only one variable was retained and subsequently these were taken as independent variables.
The entire data set was used for the analysis using GenStats all-subset regression routine and the best
d l l t d ( i 13 1) I t f th t f h l t i bl
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2.7 Dynamic simulation of crop performance and nutrient balances at field
scale
2.7.1 Model for dynamic simulation at field scale: FIELD
In this thesis two models for simulation of crop yields were used: FIELD for cassava yield simulations and
QUEFTS for maize yield simulations. In this section both models will be discussed, but the model FIELD
will be discussed more elaborately because of its importance in the modelling in this thesis.
To be able to explore short to medium term consequences of management options on cassava yield and
soil fertility indicators a model was used. Several models on cassava crop production exist but as stated
in research done by Fermont (2009) none of them has been calibrated for African conditions. A model
FIELD was developed as a crop and soil sub model of FARMSIM, which is a bio-economic model
developed to analyse tradeoffs between farming systems and environments focusing on strategic
decision-making and embracing the spatial and temporal variability of smallholder systems (FArm-scale
Resource Management SIMulator;www.africanuances.nl)(Tittonell, 2008). In overall FARMSIM consists
out of the components FIELD (crop-soil), LVSIM (livestock) and HEAPSIM (manure) modules that are
functionally integrated and allowing for feedbacks between these entities on farm scale (Figure 6). In
this thesis only the crop-soil component FIELD will be used.
FIELD focuses on long-term changes in soil fertility (C, N, P and K interactions between nutrients) which
determines crop production. It simulates crop responses to management interventions such as mineral
fertiliser, application of manure or organic amendments. Different fields within the farm are treated as
separate entities with their own set of soil properties.
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Crop biomass is calculated based on the intercepted amount of photosynthetically active radiation (PAR)
which is only a fraction of total PAR during the growing season. Light determined yield can
subsequently be estimated by using a light conversion efficiency coefficient and is affected bymanagement factors such as cultivar choice, planting density and planting time. Water-limited crop
production is calculated based on seasonal rainfall data and site and crop specific water use efficiency
coefficient and therefore depends on data availability of the study sites and has to be derived from
literature otherwise. Nutrient-limited crop production is calculated from nutrient availabilities and
nutrient use efficiency of the crop. Other nutrient sinks for example leaching and gaseous losses of N or
immobilization in the soil organic matter act as competition components to crop uptake an can be used
to derive the nutrient capture efficiency of the crop. To be able to calculate resource-limited cropproduction in FIELD the minimum of water-limited and nutrient limited crop production (determined by
the availability and use efficiency of N, P, K and their interactions ) has to be taken following Liebschers
Law of Optimum (Van Keulen, 1995). Reduction factors such as weed competition are used to calculate
actual yield and derived from multiplying actual biomass production with a harvest index coefficient
(Tittonell, 2008).
A sensitivity analysis can be used to study the relative variation in model outputs in response to changes
in model input or parameters. The model was run on a number of fixed parameter settings presented in
Appendix Table A 12. The relative partial sensitivity of the model input can be calculated with the help of
following equation (Tittonell, 2003):
(dO/O) / (dI/I)
In this equation (dO/O) is the relative change in model output and (dI/I) is the relative change in the
value of parameter or input data. Sensitivity was calculated as the average sensitivity to changes in thevalue of parameters that were set according to information from the field (if available) or systematically
(e.g. increase and decrease of 10%). Calibration, validation and the sensitivity analysis have been done in
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2.7.2 Developing scenarios
The modelling part of this thesis focuses on cassava, the major staple food crop in the farms under study
in Central to North Mozambique. In the simulation no distinction for different genotypes was made sothe outcomes are the result of an average performing cassava genotype.
Crop management
The model was run for six different regimes affecting short- and long term crop and soil productivity
listed in Table 4 : 1) no input farm practise, 2) increasing cassava residue returned to soil, 3) increasing
amendment of maize based organic residues, 4) increasing amendment of on farm manure, 5) increasing
amendment of NPK fertiliser, 6) increasing amendment of NPK fertiliser plus manure and organic
residue amendment. For each management regime the model was run for all fields sampled in both
villages (N=90) for a period of 10 years. A list of fixed model parameter input can be found in the
Appendix A 12.
ManureNutrient input from manure application was calculated by the production of manure (kg year -1 animal-1),
the dry matter content and the N, P and K fractions in the model. Animal manure production was
Scenario Name Quantity
I No input -
II Cassava residues 10% and 55% remaining in the field
III Maize residues 1-5 t/ha (steps of 1 t DM)IV Small stock farm manure 0.125, 0.25, 0.5, 0.75, 1.0 t DM ha
-1
V NPK fertiliser 25, 50, 100, 150, 200, 250, 350 kg ha-1
VI Improved NPK management NPK + 0.25t DM ha-
manure + 1t DM ha-
pigeonpea residues
Table 4. Overview of management scenarios applied
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literature for the different crop residues used in the management regimes. For the purpose of the
different management regimes two types of residues were used: maize and pigeonpea. The amount of
nutrient in the residue was estimated using literature choosing a medium nutrient composition formaize, and an upper nutrient composition for pigeonpea. For maize 1%N, 0.2%P and 1%K was used
derived from work done by Dass (1979). For pigeonpea a high nutrient content of 4%N, 0.4%P and 4%K
was estimated to represent a hypothetical high nutrient rich legume. Lignin content was taken from
literature at rates of 5.4% and 10.7% and of total DM content for maize and pigeonpea (Bernard and
Jean-Marc, 1986) for maize and (Mapfumo and Mtambanengwe, 2004) for pigeonpea.
For maize farmers estimations on maize yield and QUEFTS simulations were used to calculate maize
biomass production and an HI of 40% was derived from work done by Hay and colleagues (2001). The
effect of cassava residue incorporation was simulated in two scenarios: 10% and 55% cassava residue
incorporation. 10% remaining residue complies with standard farm practice of removing all crop
residues and having some remains (in e.g. litter fall or some stalk remaining). The proposed 55% cassava
crop residues is in line with harvesting the tubers and stalks for planting but leaving the remaining stems
and leaves (instead of e.g. burning). Lignin content was assumed to be 8.4% of total DM and nutrient
content of crops residues set at 1.2% N, 0.2% P and 0.7%K , derived from Putthacharoen et al.(1998).
Table 5. Nutrient amendment in scenario simulations
Maize1
residues
Cassava
residues1
Pigeonpea1 Small stock
manure
HI 40 45 30 -
DM (%) 64 26 53 50Per ton DM applied
N (kg/ha) 9.0 12 36.0 20.0
P (kg/ha) 1.8 2 3.6 4.0K (kg/ha) 9.0 7 36.0 20.01Fraction incorporated was set at 0.9 (meaning 0.9 t of every ton added to the soil gets incorporated into the soil)
F tili
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3 Results
3.1. Characteristics at village levelThe following section (Section 3.1.1) analyses results found at village level: comparing between the
villages Nacuaca and Gafaria for bio-physical variability.
3.1.1 Village biophysical variability
Average value of soil fertility indicators varied between villages in the district as predicted by the
variation in inherent soil types present. For most important soil fertility variables, box-plots are
presented in the Appendix Figure A 1, determination and calculation of the soil fertility variables used
can be found in the Appendix A 3. Comparing fields under cultivation between villages showed a
significant higher percentage of clay content in Gafaria compared to Nacuaca (25% compared to 12%,
P
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Table 6. Percentage of fields (N=90) belonging to soil fertility class Very Low (VL), Low (L), Medium (M) and High (H)
according to soil property groupings of Instituto Nacional des Investigao Agronmica (Maria and Yost, 2006)
% of fields grouped per soil fertility class
Clay SOC N P K Al saturation
Nacuaca Class
VL 12 14
L 42 75 48 17 23 66
M 58 14 52 77 52 33
H 6 12 1
Gafaria Class
VL 3
L 5 74 5 21 67
M 87 24 92 79 45 31
H 8 3 55 2
Villages P< 0.001 ns 0.001 ns 0.007 ns
Fields of Gafaria were found significantly higher in exchangeable K (cmol(+) kg-1) compared to Nacuaca
with an average of 0.46 compared to 0.21 cmol(+) kg-1 respectively (P
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Figure 8. Exchangeable K (cmol(+) kg-1
) plotted against clay content for all soil samples
combined (N=90) for Gafaria and Nacuaca
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Sampled fields in both Nacuaca and Gafaria had a comparable pH, but the pH range of fields sampled
differed: a wider range was found in Gafaria (pH 5.3-6.8 for Nacuaca and pH 4.9-7.4 for Gafaria). None of
the fields sampled was classified as extremely acid (>4.5). 10% compared to 37% of the soils wereclassified as strongly acid (pH 4.5-5.5), 87% compared to 55% as slightly acid to acid (5.5-6.5) and only 2
samples from both villages were classified as neutral (6.5-7.3) in Nacuaca and Gafaria subsequently
(Table 7).
No differences were found for the Cation Exchange Capacity (CEC) of soils comparing both villages with
an average of 24.6 cmol kg-1 for Nacuaca and 26.0 for Gafaria. The Exchangeable Cation Exchange
Capacity (ECEC) was found to be an average of 10 cmol kg-1 for both villages. Base saturation (the sum of
bases Caexch, Mgexch, Naexch and Kexch/ECEC) did not differ significantly with a total average of 67% in both
villages.
Aluminium saturation (Alexch/CEC*100) can be an important indicator of aluminium toxicity on acid soils
and is considered low, medium and high at ratios of 0-15, 15-35 and >35% aluminium saturation. Of the
soils sampled 67% compared to 79% were classified as low and 33% and 21% as medium in Nacuaca and
Gafaria (Table 6).
Table 7. Percentage of fields grouped in the different pH ranges presented for Nacuaca and Gafaria (N=90),
classification used is derived from the Institute of Agricultural Research (Appendix Table A 2)
% of fields
pH range Nacuaca Gafaria
4.5-5.5 10 37
5.6-6.5 87 55
6.6-7.3 4 5
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3.1.2 Socio-economic variability at village level
This section focuses on results found at village level: comparing between the villages Mugema, Nacuaca
and Gafaria for socio-economic characteristics, production activities and managerial aspects.
The farms sampled in this study showed characteristics in terms of family structure, income sources and
farm indicators that could consider them as representatives for the study area as compared to the
results of the baseline study conducted in the area (OVATA mid term, 2004). All results in this
subchapter are based on the total data set of farmers (N=74, three villages) unless indicated elsewhere.
Comparing villages no difference was found in the number of household heads being illiterate: anaverage of 11% of farmers per village did not go to school and had no knowledge how to read or write.
The remaining rest differed in level of education from 1st class until 8th class as highest education
(Appendix Table A 5). Men were more likely to have a higher education compared to women across
villages, females had a higher illiteracy rate compared to males across villages (not shown).
Sampled farms showed differences as well as shared characteristics across sites, some of these
characteristics are shown in Table 8 below. The average amount of fields per household was significantly
higher in Gafaria compared to farmers in Mugema (3.7 compared to 2.6 respectively). Household
members, the amount of people present at the farm, did not differ across sites with an average of 6-7
family members.
Closest fields for all study sites were 1.0-1.5 min walking away from the homestead. These fields would
be in the immediate vicinity of the family houses and storage sheds. Farmers of Gafaria all had their
fields close by the house (25 minutes) whereas on average 154 minutes had to be walked to reach the
furthest field in Nacuaca, Mugema was found intermediate with fields on 50 min walking distance.
The total amount of animals (including all animals) per household compared between study sites did not1
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Table 8. Socio-economic indicators and production activity indicators per household for the three villages of study
(N=74)
Site
Indicator unit Mugema Nacuaca Gafaria P
Socio economic indicators
Household members present # 5.6 6.7 7.0 ns
Amount of machambas # 2.6a
3.2ab
3.7b
0.011Distance to closest field min 1.0 1.5 1.0 ns
Distance to furthest field min 50a 154b 24a 0.003
Months without food # .7a 1.3a 3.7b 0.001
Total income out of agriculture MZN1 5853ab 12286b 878a 0.038
that hire labour % 28 29 10 ns
that have off farm income % 44 21 41 ns
Production activity indicators
crops grown # 6.2a 7.2b 7.9b 0.009
cash crops grown # 1.0 1.0 1.0 ns
Fruit trees grown # 9.4a 11.6a 26.0b 0.001
Households that own animals % 80 92 92 ns
Households that own livestock % 48 67 64 ns
number of animals # 11.8 10.4 9.2 ns
number of goats # 1.0 9.7 5.0 ns
number of pigs # 5 2 4 9 6 4 ns
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Food (in) security
Farmers were asked for the number of months per year with food insecurity/shortage. Respondents of
Mugema were able to feed themselves in average all year except for 1
month, respondents in Gafaria had a significant higher amount of months with food insecurity (3.7
p
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Table 10. Start and end month of food insufficiency indicated by the respondents (% of households) in Mugema,
Nacuaca and Gafaria (N=74)
Mugema Nacuaca Gafaria
N 25 24 25
Start August 4 0 0
October 4 4 12
November 4 13 52
December 12 17 16
January 12 29 16
February 0 8 4
March 4 0 0
no hunger 60 29 0
End April 8 0 8
May 0 4 16
June 0 0 4November 4 0 0
December 12 8 0
January 4 0 4
February 4 46 20
March 8 13 48
no hunger 60 29 0
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Labour
Labour was mainly derived from the household although some farmers from the survey also hired
labour from outside the farming household. Between 10 and 29% of the farmers hired labour on aregular and non-regular basis to relief pressure during the peak season of labour for preparing the fields
and harvesting of maize. Farmers themselves would work for their neighbour (ganho-ganho) at times of
hunger and get payment in food. Most commonly the whole family or the wife and husband contributed
to the largest part of the labour provided by the family (Table 11).
Table 11. Household members contributing the most to farm labour (percentage per household, N=74)
SiteTotalMugema Nacuaca Gafaria
N 25 24 25 74
Who works the fields the
most?
wife 8 8 5 7
wife and husband 40 75 33 50
whole family 40 8 48 31
husband 0 4 0 1
wife and children 12 4 10 9
wife and grandmother 0 0 5 1
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Household income
Total household income was calculated summing the considered three main sources of income: income
from crop production, income from animal production and off farm income. The percentage ofhouseholds being involved with activities belonging to the different sources of income are listed below
in Table 12. Although no significant difference could be found in the amount of households being
involved in the different economic activities mentioned, a difference could be found in the percentage
off farm income contributed to total calculated household income comparing between villages. For 44%
of the farmers involved in the survey from Gafaria off farm income contributing for an average of 75% of
their total household income. For Mugema and Nacuaca 44 and 21% of the households had sources of
off farm income, contributing to 19% and 21% respectively of their total calculated household income.Off farm income activities mentioned were making crafts (45%: such as blocks, sieves or stoves), being a
middleman (21%: selling maize or beans) or working for others (14%), remittances or pensions were
received by the remaining 21% (N=29 out of 74,Table )
Table 12. Percentage of farms within the farm samples from the three sites that are involved in activities listed
below and their proportion of total income (N=74)
VillageMugema Nacuaca Gafaria
% of households selling animals or animal products 28 33 40
% of households selling crops 96 83 100
% of households having sources of off farm income 44 21 44
% of income from animals or animal products 9 12 17
% of income from crops 72 81 50
% of income from off farm 19 21 33
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Income from crop production
Importance of on farm income from crops differed between villages: 72 and 81% of total income in
Mugema and Nacuaca was derived from crop sales compared to 50% in Gafaria (see Table 12 ).Households of Gafaria in average had the lowest income from agriculture compared to Mugema and
Nacuaca (878 compared to 5150 and 12285 MT hh-1; Table 8) and a higher percentage of income
attributed by selling of the alcoholic drink Ortega (37%, Figure 10). Ortega is an alcoholic beverage made
from cassava and sorghum flour as ingredients, fermented for about a week and a medium to high (
12-20%) alcohol percentage. A significantly higher percentage of farmers were selling Ortega in Gafaria
compared to farmers in Nacuaca and Mugema. Farmers in Mugema had a considerable higher
percentage of beans sales contributing to their from farm income (35% P
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Table 13. Percentage of farms selling the most commonly grown crops and beverage Ortega listed below in the
three villages (only farmers growing the crop have been included see Table 12)
Table 14. Frequency of farmers (%) selling cassava and maize to listed buyers below (N=17)
Site
Mugema Nacuaca GafariaP 2). However to
be able to purchase NPK fertiliser farm households need capital for investment. Farm type 1 and 2farmers seem to have more capital available from crop and animal sellings (Figure 11). Farm type 3 has a
much higher percentage of income out of non-farming practises and doesnt seem to be as highly
dependent on agriculture, like the other farm types. As they do have capital to invest, they might lack
the involvement and expertise required make investments in agricultural inputs such as fertiliser. Farm
type 4 farmers are mostly single headed households that are not as involved in farming for income
generation, but mostly to support themselves and the remaining of the family present. Typologies found
in this research seem to be in line with characteristics of typologies found in previous research byTittonell (2009).
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Improved management simulations included manure, crop residue and fertiliser in a complete
application package. The feasibility of this package requires availability of manure. Comparing farm
types, Type 1 and 2 farmers in general had the highest number of animals available on farm and were
more likely to own small stock (goat or pig).Figure 22 tries to illustrate capital availability on farm and animals present classified per farm type.
Farm types 1 and 2 seem to have as well a higher number of animals, as more capital for investment.
From literature the hypothesis is proposed that farms having on-farm income strategies (Farm type 1
and 2), are more focused on productivity and often more innovative. They can be characterized by an
earlier adoption and adaptation of technologies and could serve as an example for other farmers in the
community. Reij and Water-Bayer (Reij and Bayer, 2001) even state that this may even facilitate the
further outspread of technologies in the community.
5.1.5 Model FIELD considerations
Simulated yield response by the FIELD model used in this research was only influenced by the soil
fertility of the different fields used (N=90). Other variables such as weed management, pest and disease
pressure and harvest age have not been included in the simulation, while previous research showed
fertiliser response affected by soil fertility, rainfall and weed management (Fermont et al., 2009). It is
therefore important to look at the simulated result from the viewpoint of soil fertility alone, keeping in
mind several other variables that can influence actual yield.
Extra demand in labour, for the scenarios involving crop residue incorporation and manure applications
have not been taken into account in this study. Several attempts were made to quantify labour needs,
but did not succeed in sufficient and reliable data. Especially for cassava residues, which can be difficult
to handle in the field, extra labour could be required to cultivate the same field size. Even so, the size offield could suffer under the implication of cassava residue incorporation. At this stage of research, these
remain uncertainties.
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5.2 Evaluation of feasibility
5.2. 1 Potential crops for biofuel; cassava, maize and sorghum
Firstly the discussion of cassava as a biofuel crop will be focussed upon: being the most important crop
of this study. Sorghum and maize will be used to illustrate and elaborate on the biofuel discussion. This
thesis can merely provide with insights from research done in three villages as case studies in Alto
Molcu district.
Ranked as the most important crop by 60% and 70% of the respondents in Nacuaca and Gafaria
respectively, cassava plays an important role for farmers in the research villages. As discussed before
one of the main advantages of cassava is the storing of roots in the soil. While other crops such as maizeand sorghum have a more defined time frame of harvest, cassava can be kept undisturbed for a later
period of harvesting. Only one third of the farmers in Gafaria (26%) sold cassava compared to 42% in
Nacuaca and 48% in Mugema. When sold cassava was sold as less than half of the produced quantity:
47, 49 and 43% respectively for Mugema, Nacuaca and Gafaria. From the interviews it was understood
that mostly cassava is sold within the community (82%) but some was also sold to people coming from
far (18%). If farmers would be involved in a emerging cassava for biofuel market, with current
production levels, the surplus being sold to neighbours with insufficient cassava production at themoment, could be sold for biofuel purposes. This could be an important consideration to be investigated
in further detail. The resilience of a community for food insecurity can be outbalanced if cassava is sold
outside the community. Currently low priced (contributing to an average of 12% of total income)
cassava could increase in value because of extra demand of the market from the biofuel industry.
Therefore making it more expensive as a food crop purchase for cassava consumers.
As an illustration the crop maize can be used. As well as an important food crop, maize also serves as a
commonly used crop to generate cash. Recent programmes such as People for People (PforP) try to
increase food security in Mozambique and surrounding countries by buying farmers surplus of maize,
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bottleneck in the adoption of sweet sorghum cultivation. However, since farmers are familiar with
sorghum growing practises, sweet sorghum could be introduced not as a crop to replace sorghum but as
an extra cash crop. The same way, sesame has been introduced a couple of years ago to generate cash
for the farmers while hardly being consumed.
The biggest question remains if current cassava yields can be increased. This thesis has discussed ways
to increase yields starting from low capital required residue and manure applications to higher capital
investments needed if fertiliser would be applied. Previous research has shown that only 4% of the
farmers have access to credit, although rural banks are emerging and more micro-credit incentives are
being developed (MINAG, 2007). Outgrower schemes for e.g. the production of tobacco are excisting
and providing farmers with fertiliser under contract production. These existing outgrower schemes
could provide with examples and frameworks on how commercial firms can arrange input purchases or
input credit for farmers under production contracts.
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5.3.Methological considerations
5.3.1 The use of a farm typologyInitially after the first rapid farm characterisation (May-June 2009) a farm typology was designed to
characterize farm types and have a better understanding on within and between village farm
heterogeneity (and homogeneity). This first typology was based on dividing farmers on farm income,
their involvement in farming and several wealth indicators as suggested by experts (amount of animals,
hired labour, maize and bean production). A total of 5 farm types were identified for all three villages
(Mugema, Nacuaca and Gafaria) and 2 farmers per village were selected for re-visit (excluding Mugema).
After returning from fieldwork and the start of analysis questions arose about the correctness of the
chosen typology. Ideally, a chosen farm typology should capture the most important characteristics that
would typify farm households according to their similarities within a typology and their dissimilarities
between typologies. A re-evaluation was made using the proposed methodology presented in Chapter
2.2.2. After designing the new typology, more profoundly based on the results of the rapid farm
characterisation, and making divisions in farmers based on several variables and less strongly on farm
income it was found that on revisiting the selected farmers a farm type group appeared under sampled.
Farm type 3 farmers characterized by high off farm involvement seemed to have been not re- visited in
sufficient amount in Gafaria and even more in Nacuaca where farm type 3 was left out totally (Appendix
Table A 18). The first farm typology design was mainly based on variables presented in Appendix A
19.where a separate typology was made for farmers hiring labour. As shown farm management
practices such as burning of crop residues were taken into dividing farmers over typologies. Pros and
cons for both types of typologies can be thought of but keeping in mind the function of a typology in
this research: a tool for understanding variability between farmers within a village, the revised typology
seems to have a more profound basis, even though sampling has been done with a less favourable
division.
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5.3.2 Yield estimations
Yield estimations in this study were done following several methods as presented in Chapter 2.4 and
listed in the Appendix Table A 8, Table A 9 and Table A 10. For cassava three methods were used to
estimate production/ha. Because of limitation in field work, only a limited amount of plants could be
harvested per plot, calculations from harvest measurements remain uncertain. Previous research done
by Hilton (2000) showed farmers underestimating their yields by 25-50%. This would imply that actual
yields should be considered somehow in between the range of (lowest to highest): estimated by farmers
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6. ConclusionsInitially the aim of this study was to explore smallholder farming systems producing cassava, maize and
sorghum in the scope of the current raging discussions on crops for biofuel production. Although
Mozambique has been identified as a promising country for biofuel production little is known about
current farming systems.
An important finding of this research was the high heterogeneity found comparing villages and within
villages. Analysis at different levels: village, farm and field provided helpful tools and the design of a
typology helped to analyse within village variability. An interdisciplinary approach in which bio-physical,
socio-economic and farm management practices was used to explain variability can be considered key to
this sort of research. As an example the case study of Gafaria can be mentioned: based on bio-physical
analysis alone Gafaria would be thought to be more fertile and higher in production compared to
Nacuaca. From socio-economic analysis the opposite was found: farmers in Gafaria seemed to be less
well off compared to farmers in Nacuaca.
Cassava yield estimations, currently lacking in many research projects, have proven to be very difficult in
this research. Initially the aim was to quantify yields of cassava, maize and sorghum but due to severalunforeseen circumstances this could not be accomplished. Therefore explaining current yields in relation
to soil, landscape and management variability was not possible. This is to be regretted because it could
have provided with important insights on most important factors, besides bio-physical properties,
limiting yields.
As a result of this, simulated cassava simulated yields by the model FIELD, are based on soil fertility
alone and not on interactions with crop management such as weeds and pests. It is a major limitation
that has to be taken into account. Simulated yields of FIELD were higher than estimated yields by
farmers but lower than calculated yields from field work. Harvest measurements are lacking to assess
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The development of cassava for ethanol could strongly increase the demand for cassava and could be an
incentive for farmers to adopt technology packages to improve productivity and profitability of cassava
production. However which farmers would be more suitable to involve in production increasing
activities (e.g. the adoption levels of farmers to improved techniques) could be assessed with the help of
farm typologies. Considered solely as a tool they can provide with insight on important farm
characteristics and could be used in allocating promising pilot projects. Production orientation, resource
possibilities and farm involvement could be important indicators derived from a Farm typology. Four
different farm types over the three villages were identified in this study. From this research Farm Type I
and II would be indentified as feasible candidates for pilot projects.
Within farms it was found that fields could be classified into quartiles corresponding to FIELD simulatedyields. 4th quartile fields seemed to be more responsive to any nutrient amendment (in-organic and
organic) and had overall higher yields compared to 1st and 2nd & 3rd quartile fields. Allocation of available
nutrients to these higher producing could induce soil fertility gradients over farms and should be taken
into consideration.
Recommendations
This study has provided insights in farming systems from three villages in Alto Molcu district, Northern
Mozambique and can underline the importance of studies focused on exploring the farming system.
Biofuel projections are based on assumptions and estimations on national level, with 80% of the
population of Mozambique being involved in agriculture one can imagine the heterogeneity in
possibilities for production.
On farm improved farm management trials could provide with more insights on factors affectingyields such as weeds, pests and diseases. The model FIELD could be improved and further
calibrated to have a better fit; it could provide as a helpful tool in simulation of different
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