Previous Page Table of Contents Next Page


Chapter 2 SYSTEMS ANALYSIS, A SPATIAL APPROACH


From the introduction it is clear that understanding existing animal production systems is a keystone of any decision-support system. Therefore, the initial step undertaken was to produce a spatial inventory of livestock production systems prevailing in West Africa within their respective ecogeographical settings. Underlined system dynamics are discussed by comparing spatial patterns with recognized livestock production systems.[2]

Climate, livestock and agriculture

In any given ecogeographical setting the occurrence and development of livestock production systems can be described by three main factors: human population density, crop agriculture intensity and livestock density (FAO, 1997). While population maps at a useful resolution and at continental scale already existed (e.g. Center for International Earth Science Information Network [CIESIN]),[3] only recently has a continental 5-km grid data set, including satellitederived cropping[4] intensity and cattle distribution layers, been developed and made widely available (PAAT-IS).[5] The availability of such data layers allows the study of distribution patterns of single and combined variables at a subnational scale. The patterns observed and trends derived may prove invaluable for the understanding of occurring and current drifts of livestock production systems and for the planning of adequate pest management.

FIGURE 1
Crop-livestock systems in West Africa

Observed crop-livestock systems patterns (central map) clearly show centripetal mixed farming aggregations around development poles. From east to west - Kano and Jos Plateau in Nigeria, Ougadougou in Burkina Faso and Dakar in Senegal. This is confirmed when comparing average population density numbers for each mixed farming type. See Box 1 for background information.

A study jointly initiated by FAO and IAEA aimed, inter alia, at analysing these patterns for West Africa (Hendrickx, 2001). Results obtained are summarized in Figure 1 and some methodological aspects are discussed in Box 1. The analysis revealed a set of distinct patterns (Figure 1, central map):

BOX 1

Spatial definition of livestock production systems: some methodological aspects

1. Five-km raster data layers for agriculture intensity (mainly cereals, no data on tree crops and tubers included) and livestock density were reclassed in three classes (high, medium, low) based on expert knowledge.

2. Both data layers were overlayed (cross-tabulation principle) using commercial GIS software (Idrisi 32) and unique values were given to newly created classes, thus defining livestock production system categories, e.g. category medium cattle AND medium crops = mixed.

3. Based on the length of vegetation growing period, the northern pastoral band was defined.

4. Livestock production system categories were further grouped according to the emerging patterns and agro-ecological setting:

  • Northern arid and pastoral band

  • Central mixed farming band

  • Southern humid crop band

5. Average human population densities were calculated per livestock production system category to contribute to the system dynamics analysis.

6. The occurrence of a known set of physical constraints (International Institute for Applied Systems Analysis [IIASA]) was estimated per livestock production system category.

As described above, the different livestock production system categories are not randomly scattered but a distinct north-south band-like pattern emerges. The given average population density figures per production system further highlight an overall humaninduced dynamic pattern of higher intensity linked to higher density (Figure 1, arrows). These findings can now be compared with livestock production systems as described in the LEAD (Livestock, Environment and Development initiative of FAO) toolbox (Box 2). It is important to note that these systems rarely occur in a separate fashion, but overlap in expanse.

BOX 2

FAO-LEAD livestock production systems classification

A set of livestock production systems is described per agro-ecozone in Figure 1 on page 6. Dominant West African systems are summarized below.

1. Grazing systems: highly dependent on the natural productivity of grasslands.

a. Mobile systems

  • Arid: nomadic or pastoral communities respond with mobility to environmental variability.

  • Semi-arid: pastoralists must have access to communal pastures along the circuit of transhumance. Though agreements are concluded for resource sharing leading to mutual benefits, conflicts may occur.

  • . Subhumid and humid: in these zones the majority of livestock owners are sedentary. The remaining mobile pastoralists mainly use natural resources in remote areas with low population density.

b. Sedentary systems: as an adaptation to prevailing conditions pastoralists can move to mixed farming and abandon transhumance but remain by profession livestock farmers.

  • Semi-arid: sedentary livestock farmers earning most of their income from livestock and giving more attention to livestock than to crops. Agreements are made with other agriculturists but crop encroachment disrupts pastoral areas and limits access to water.

  • Subhumid and humid: as a result of population pressure and increased disease risk sedentary grazing is less common. Mostly found in regions where the population pressure is high or increasing. Part of the livestock is owned by outsiders.

2. Mixed systems: conducted by households where crops and livestock are more or less integrated components of one single farming system.

a. Mixed communal grazing: communal grazing areas are the principal feed resource base for livestock, crop residues are grazed and animals are kept in a kraal at night. Farmers remain crop farmers by profession. The principal production objective is to keep livestock as a savings account and to produce milk. Most cattle are kept in village herds.

b. Mixed systems using crop residues: crop residues are collected and conserved to feed livestock on the farm. Part of the year livestock are still grazed on communal areas. The composition of herds by species and animal type may be changed - more draught animals, relatively more goats, sheep grazing fallow and productive cattle on farms.

Major physical constraints to agriculture

One step further in understanding the evolving livestock production systems and the integration of cattle and crop agriculture, should the tsete and trypanosomiasis constraint be removed, could be achieved by analysing the potential environmental risks of a further intensification. Based on a joint IIASA(International Institute for Applied Systems Analysis)-FAO data set (FAO/IIASA, 2000), major climatic and physical obstacles to agricultural activity were mapped (IAEA, 2002). When combined with agriculture intensity, such data layers help highlight areas where soil degradation is a major risk at the regional level.

Results obtained are summarized in Table 1 and areas where physical factors are major impairments to crop agriculture development are depicted in Figure 1, bottom map. In general more than one-third (38 percent) of the total land area in West Africa copes with some form of major physical constraint to agriculture. Poor soil fertility is the most common problem (more than 25 percent) further stressing the urgent need for improved mixed farming practices in the entire area.

In conclusion, the farming systems’ analysis briefly outlined above revealed an important set of patterns. Livestock production systems appear not to be scattered but distributed in a band-like pattern throughout West Africa. The general agro-ecological setting, including climate and vegetation, appears to be the driving force behind this. The described analysis, i.e. spatial distribution patterns and levels of human density and livestock-agriculture intensity, contributes to a better understanding of the dynamics of production systems. Historically, livestock and crop agriculturists have developed different strategies to address the tsetse problem, for example, herd management and use of trypanotolerant domestic breeds together with trypanotolerant and trypanosusceptible crosses. Crop encroachment on tsetse habitat in areas of higher crop intensity and the widespread use of trypanocidal drugs allowed for influx of trypanosusceptible breeds in the semi-arid and subhumid agroecozones. Trypanotolerant livestock breeds are still the dominant breeds in the more humid agro-ecozone. These different agroecological settings should be duly considered in designing T&T control strategies.

TABLE 1
Percentage areas with major constraints per crop-livestock system

System

Slope

Soil texture

Soil depth

Chemical

Fertility

Drainage

Any physical constraint


1.5%*

8.5%*

7.1*%

4.5*%

26.4*%

6%*

37.9%*

Southern crop band








Moist perennial

1.8

1.3

3.6

2.4

75.3

4.3

78.7

Crops medium

1.6

4.7

6.1

4.5

49.4

8.1

56.1

Crops high

3.0

11.3

4.7

7.4

29.5

19.0

53.2

Pastoral arid plains








Arid/semi-arid

0.2

31.3

15.6

13.6

15.8

15.7

40.1

Pastoral arid

0.4

18.9

9.5

12.1

12.3

11.8

34.3

Cattle systems








Cattle medium

2.7

8.5

14.6

2.0

37.8

4.3

54.3

Cattle high

7.0

6.8

8.2

5.6

47.8

8.6

63.6

Mixed systems








Mixed

1.6

9.8

7.2

4.5

18.6

5.8

35.7

Mixed cattle

3.2

10.0

9.3

5.3

19.3

10.5

42.6

Mixed crops

1.3

11.2

2.3

6.1

8.0

5.4

28.1

High intensity

2.7

6.0

4.7

5.6

20.2

5.5

34.4

* percentages mentioned in top row indicate total land area percent affected by respective constraint in West Africa


[2] Livestock and Environment Toolbox, FAO-LEAD, http://lead.virtualcentre.org/ en/dec/toolbox
[3] Found at http://www.ciesin.org
[4] Training data used to produce satellite-derived cropping-intensity prediction are mainly based on cereal crops and often do not include tree crops and tubercles. Therefore this layer is referred to as cereal cropping
[5] Found at http://www.fao.org/ag/againfo/programmes/en/PAAT/home.html

Previous Page Top of Page Next Page