Livestock Research for Rural Development 26 (6) 2014 | Guide for preparation of papers | LRRD Newsletter | Citation of this paper |
This study was conducted to investigate challenges of integrating livestock into organic pineapple farming so as to develop strategies to enhance integration of livestock for purposes of improving soil fertility for sustainable organic pineapple productivity among smallholder farmers. Such sustainable integrated production of crops and livestock was envisaged to improve quality of organic pineapples and animal products that can easily tap into niche organic markets. Using a semi-structured questionnaire, individual interviews were conducted among selected smallholder certified organic pineapple farmers in Kayunga and Luwero districts of Uganda.
Results showed that the organic pineapple farms in the study area varied widely. Average farm sizes were 4.8 acres in Kayunga and Luwero district. Farmers in both districts used family labor (72%) for most farm activities. However, hired labor was employed during periods of planting, weeding and harvesting of pineapples. The farms kept different livestock species mainly cows, goats, pigs and chicken. Majority of the organic farms in Kayunga (37.8%) and Luwero (41.5%) had two livestock species of mostly indigenous breeds. Tethering was the most common management system for ruminants while chicken and pigs were kept on free range. Chi-square tests showed a significant (P<0.05) relationship between management system and the breeds of cattle kept in the study area. Most indigenous breeds were tethered while cross breeds were zero grazed. The most common animal feed resources were natural pastures and crop residues.
Challenges encountered by the smallholder farmers were mainly feed shortages in the dry season, livestock pests, diseases and limited knowledge on organic husbandry practices. The major pests and diseases included helminths, ticks, East Coast fever and Newcastle disease. Despite being organic farms, the use of synthetic chemical drugs still remained the major intervention for animal disease control. The presence of non-organic herds and certified organic pineapple crops within the same production unit as well as pests and disease challenges to livestock production were identified as major obstacles for integrated crop-livestock production among the smallholder organic farmers. A move towards having organic farms orientated towards organic livestock production will possibly enable farmers benefit from a fully integrated organic system with the benefit of accessing niche markets for the organic animal products. Infrastructural development, research and improving farmer’s education are suggested strategies that might support integrated smallholder organic pineapple production.
Keywords: certified, farming system, nutrient recycling, organic principles, productivity, organic livestock production
The world is under substantial pressure to reduce food insecurity, soaring food prices and deepening poverty due to the projected increase in human population of about 8.3 billion by 2030 (UNPP 2008). Increased population will certainly result into increase in demand for food and shelter which will otherwise impact on agricultural farming systems. There will be a need for more intensified systems as a result of multiple and competing pressures for producing feeds for livestock and food for human consumption (Herrero et al 2009a; McDermott et al 2010; Udo et al 2011). Since much of livestock production is generally more resource demanding, there is a great need to ensure that it develops in an economic but sustainable way which includes integrating animal production into existing crop farming systems and ensure local nutrient cycles. The newly established livestock-crop farming systems should then lead to increased food production without degrading the natural resources. Well-integrated systems may also be more environmentally friendly by producing animal feed or using by-products as feed, rather than transporting them over large distances. Livestock production systems are considered sustainable if they also support and promote animal welfare and health.
Crop-livestock systems are a backbone of sustainable pro-poor agricultural growth in tropical countries and they provide majority of the world’s milk and meat (Herrero et al 2009b; Herrero et al 2010; Wright et al 2011). Integrated crop-livestock systems revolve around the interactions of crop and livestock enterprises, for example with livestock providing draft power to cultivate the land and manure to fertilize the soil, and a diversity of crop residues as feed for livestock. However, in some instances mixed crop-livestock systems are not necessarily integrated especially where livestock production is only considered as a way of averting risk in case of crop failure. In both cases smallholder farming systems with mixed resources are challenged with how to ensure increased food production without compromising natural resources and rural livelihoods (Herrero et al 2010). Organic agriculture and food systems provide an interesting case of smallholder farmers’ intensification which not only gives possibility for income generation when markets involving premium prices for organic high value foods are available but also provide improved food security and natural resource management (Halberg et al 2006; Badgley et al 2007; Bolwig et al 2009; IAASTD 2009).
In Uganda, the majority of smallholder farmers operate mixed crop-livestock systems. The National Livestock Census revealed that 4.5 million households kept at least one type of livestock with the major ones being cattle, sheep, goats, pigs and poultry (UBOS 2012). Smallholder organic pineapple farmers keep livestock, however, their livestock production is rarely certified as organic and some of the animal husbandry practices do not live up to the organic principles (ie. confinement under zero grazing without room for exercise, spraying against ticks using inorganic acaricides and use of inorganic anthelmintics to control internal worms). In addition, there is no market pull for organic milk or meat. This trend needs to be solved so as to develop integrated organic farming systems. Presently, there is paucity of documented information on practices in these organic farming systems. Understanding the practices and the limitations to integration of livestock into organic crop production will give an insight into the future prospects of integrated and sustainable organic systems. This will enable development of innovative strategies to enhance integrated organic production, which will not only improve production of high value organic crops due to enhanced soil fertility, but also improve animal product quality and thus tap into the niche organic products market. The objective of this study was therefore to identify and document the practices, challenges and prospects of smallholder certified organic pineapple farmers who also keep livestock in two selected districts of central Uganda.
The cross-sectional study was conducted in Luwero and Kayunga districts in central Uganda. Both districts are principle areas for pineapple production in the country (UEPB 2005). Kayunga district is bordered by 6 districts with Luwero district to the west, it is situated about 74 km east of Kampala by road at an altitude of about 1000-1200m above seas level. Agro-economically the area relies mainly on agriculture which represents 90% of total employment. Luwero district is bordered by 5 districts including Kayunga district to the east. It is located about 75 km north of Kampala by road at an altitude of about 1082-1372m above sea level. Agriculture is also the mainstay of the district economy. Farmers in these two districts rely on rain fall for cultivation. The rainfall pattern is bimodal with the rainy seasons in March to May and October to November.
Purposeful and snowball sampling methods were used to select the study site and population, respectively, as described by Broom (2005) and Gill et al (2008). Purposeful sampling was used to select farmers engaged in production of organic pineapple but also kept livestock. A total of 90 respondents were interviewed using a pre-tested structured questionnaire. All interviews were conducted with household heads referred to as farmers in this article. These interviews were conducted in Luganda, the language used by the locals. The questionnaire included questions related to (1) demographic aspects (2) farm characteristics such as total land size, ownership and land use; (3) livestock management practices such as: feeding, breeding, manure use, diseases and pest incidences; (4) farmers’ experiences and challenges of organic farming including integration of livestock and adoption of organic husbandry practices. The questions on challenges related to integration were open ended, which allowed the farmer to explain in their own words how challenges were experienced. Other questions had a pre-defined list of optional answers where farmers were asked to give one or more answers depending on the question.
Data was analyzed by descriptive statistics using SPSS statistical package. Chi-square tests were used to assess distribution patterns of farmers’ responses in the two districts studied while T- Tests were used to assess differences related to numeric variables. Differences with P-values less than 0.05 were considered statistically significant.
Farmers interviewed included males (81%) and females (19%). The majority of the respondents had completed primary (48%) and secondary (48%) levels. In the two districts, 93% of the farmers depended on farming (93%) as their main source of income. Most households (57%) had more than 7 family members, 36% had 4-6 members and 6.7% had 1-3 members. Family labour (72%) and hired casual labour (70%) were found to be the most common sources of labour for farming activities. Farmers reported using hired labour mainly for pineapple production . Farmers indicated that the main reason for converting to organic farming was premium prices obtained from organic products (64%). Other reasons for conversion included protection of the environment (24%) and influence from the neighbors (10%). Only 2% indicated that high expense associated with use of chemicals was the reason for their conversion. Farmers derived knowledge on organic practices from different sources such as their fellow farmers (44%), companies which traded organic products (34%), NGOs (15%), extension officers (3%) and mass media (4%). The majority of farmers (63.2%) had 5 or more years of experience of using organic practice on their farms.
Average size of the farm land was 4.8 and 10.1 acres in Kayunga and in Luwero districts, respectively. The average land size and acreage under pineapples were found to be significantly larger (P<0.05) in Luwero district than in Kayunga district (Table 1). The majority ( 73%) of farmers owned land they cultivated while the minority had leases (12%) or both (13%). It was observed that organic farms had a diversity of vegetation and trees and land was divided into small plots where various cash and food crops were cultivated such as pineapples, coffee, maize beans, bananas, sweet potatoes and cassava. Major source of water for home use and livestock in Luwero district was bore holes (86.8%) while in Kayunga district it was protected wells (86%). During the dry seasons there was a risk of water scarcity in both areas.
Farmers in the two districts kept different livestock species, mainly cows, goats, pigs and chickens. Of all the species kept, significant difference was only found in the average number of chickens per farm in the two districts with farms in Luwero district having more chickens than Kayunga district (Table1). Most organic farms had two or three livestock species (Table 1).
Table 1. Least Square Means of land size, acreage under pineapples, number of animals per species and percentage of farms with number of species per district |
|||||
Parameters |
Kayunga (n=37) |
Luwero (n=53) |
SEM |
P-value |
|
Average land size (acres) |
4.77 |
10.1 |
1.26 |
0.0001 |
|
Pineapple land (acres) pineapples |
1.99 |
3.29 |
0.52 |
0.018 |
|
Number of animals per species* |
|||||
Cattle |
1.61 |
2.33 |
0.38 |
0.065 |
|
Goats |
1.86 |
2.09 |
0.48 |
0.633 |
|
Pigs |
1.91 |
0.94 |
0.49 |
0.053 |
|
Chickens |
4.85 |
8.79 |
1.33 |
0.005 |
|
Sheep |
0.13 |
0.28 |
0.22 |
0.501 |
|
Ducks |
0.46 |
0 |
0.38 |
0.238 |
|
Turkeys |
0.10 |
0 |
0.10 |
0.238 |
|
Rabbits |
0 |
0.03 |
0.05 |
0.409 |
|
Number of species per farm with figures in parentheses showing % ) |
|||||
One species |
7(18.9) |
9 (16.9) |
|||
Two species |
14(37.8) |
22(41.5) |
|||
Three species |
11(29.7) |
17(32.0) |
|||
More than 3 species |
5(13.5) |
5(9.4) |
|||
* The number of animals includes male, female, old and young stock |
Within the farm families, women majorly owned the chickens (72%), pigs (55%) and goats (56%) while men owned the cattle (72%). The majority of organic farms in the two districts reared cattle and chickens (Fig 1).
Figure 1: A graph showing the proportions (%) of organic pineapple farms owning each livestock species in both Kayunga and Luwero districts. |
Farmers had mainly indigenous breeds for cattle (62%), goats (97.8%), pigs (87.5%) and chickens (100%). Farmers reported that they crossed indigenous animals with exotics mainly to improve milk production. Natural mating was the most common method of breeding in cattle, goats and pigs in the two districts.
The most common management system for cattle and goats was tethering during the day, while in the evening animal were returned to night kraals where supplementation with crop residues sometimes was done. Chickens and pigs were kept on free range where they were left to scavenge (Fig 2). There was a significant relationship (P= 0.047) between management system and breed of cattle. The majority of indigenous breeds (74.4%) was tethered while crossbreeds (83.3%) were zero grazed. Tethering involved an animal being tied with a rope around the neck or hind leg and taken to graze in a specific area from where it is transfered to fresh grazing areas from time to time. Such animals would or would not be supplemented when returned in the evening.
Figure 2: Livestock production systems classified based on farmers’ responses on feeding and housing of animals. |
Natural pastures and crop residues were reported as the most common animal feeds in the study area (Table 2). Crop residues included: banana peels, sweet potato vines, banana pseudo stems and maize stover. It was indicated that animal feeds were either accessed from within the farms or from neighboring farms engaged in organic farming. Feed conservation was not a common practice as reported by 86% of the farmers. Those who conserved feed mainly used feed banks comprising of Napier grass. Trees which could potentially be used as fodder trees were kept on 61% of the farms: ficus trees (72.7%), Calliandra (16.4%) and Girilicida (10.9%). Farmers reported using Calliandra and Gliricidia as supplement feeds for ruminants while ficus was used to provide shade rather than for feeding.
Table 2. Types of animal feed resources offered to different animal species on organic farms in two selected districts of Uganda |
||||||
Feed resources |
Number of organic farms offering the feed resources to livestock |
|||||
Kayunga District |
Luwero District |
|||||
Cattle
|
Goats
|
Pigs
|
Cattle
|
Goats
|
Pigs
|
|
Natural Pasture |
33(100)a |
17(100) |
11(50) |
39(100) |
22(100) |
11(50) |
Improved pastures e.g .Napier |
28(85) |
12(71) |
- |
11(28) |
8(36) |
- |
Pasture legumes |
2(6) |
- |
1(2.6) |
- |
- |
|
Crop residues |
32(97) |
16(94) |
15(94) |
37(95) |
18(82) |
15(94) |
AIP |
11(33) |
4(24) |
11(69) |
1(4.5) |
1(5) |
7(44) |
Concentrate feeds |
- |
- |
0 |
- |
- |
1(6) |
Home food residues |
- |
- |
15(94) |
- |
- |
11(69) |
Fodder trees |
||||||
Calliandra |
4 |
5 |
||||
Gliricida |
4 |
2 |
||||
Sesbania |
0 |
1 |
||||
Ficus trees* |
16 |
24 |
||||
(100)a Figures in parentheses represent the percentage of farmers using a given feed resource for a particular animal species
|
Sixty four percent of the farmers had no housing for any type of livestock but kept the animals under tree shades. Only 36% of the farmers had their animals provided with roofed shelters popularly known as zero grazing units mostly made for dairy cattle. Farmers indicated that these units gave some of them opportunity to collect manure used as compost in crop gardens. Seventy six percent of farmers interviewed indicated using manure in crops like bananas, pineapples and coffee plantations.
Tethering and free-range grazing systems provided the animals with outdoor access. It was revealed that 75% of the farmers in Luwero district accessed communal grazing land compared to 25% in Kayunga district. Whereas farmers in the two districts had 20-30% of the land reserved for grazing cows and goats, farmers in Kayunga district had this land mostly allocated to planting of improved pastures for stall feeding. However, the distances between these pasture lands and the zero grazing units were reported to be long for most farmers.
Organic farmers reported various pests and diseases encountered in the different livestock species (Table 3). Among the organic farms that had cattle, helminths infestation and East Coast Fever were the most commonly experienced animal health challenges. There was a relationship between these challenges with animal breed and management system. Helminthes infestation seemed to occur more frequently (78%) in crossbreeds than in local breeds (48.3), but East Coast Fever and tick prevalence as indicated by cases reported by farmers were observed to be distributed similarly (ie in ranges of 42% - 50%) between breeds and husbandry systems. Kayunga district reported higher cases of helminths infestation and East Coast fever compared to Luwero district. But more cases of tick occurrence were reported in Luwero district (Table 3). Cattle diseases that were vaccinated against by some farmers included Trypanosomiasis (60%), Foot and mouth disease (27%) and East Coast fever (13%). Farmers who did not vaccinate animals indicated lack of service providers, yet others did not perceive it as necessary due to low risk of disease on their farms. Farms with goats reported helminthes as the major health challenge in free range (88%) and tethering (100%) systems. Farmers with pigs reported helminths and Swine fever as the most experienced health problems. Farmers who kept their pigs as free-range reported the highest cases of helminths (87.5%) and swine fever (62.5%). New Castle Disease was the major disease in chicken within free range (73%) and semi-intensive (100%) management systems. All interviewed farmers reported using synthetic veterinary drugs to control pests and diseases in livestock. However, some farmers reported use of herbal concoctions mostly in chicken. Organic farmers indicated that the continued use of conventional veterinary drugs resulted from limited alternatives available to them. Advice on treatment of livestock diseases was sought from different sources which included private veterinary practitioners (67.8%), fellow farmers (34.4%), government extension officers (15.6%) and NGOs (4.4%).
Table 3. Diseases and pests experienced in the different livestock species on organic farms |
||||||||
|
Number of respondents (%) |
|||||||
|
Kayunga district |
Luwero district |
||||||
|
Cattle |
Goats |
Pigs |
Chicken |
Cattle |
Goats |
Pigs |
Chicken |
Farmers that responded |
30 |
9 |
11 |
10 |
31 |
12 |
9 |
14 |
Diseases &pests |
|
|
|
|
|
|
||
Mastitis |
0 |
0 |
0 |
NR |
3.2 |
0 |
0 |
NR |
East coast fever |
53.3 |
0 |
NR |
NR |
48.4 |
NR |
NR |
7.1 |
Mange/Skin infections |
3.3 |
NR |
9 |
0 |
6.5 |
8.3 |
22.2 |
NR |
Milk fever |
0 |
NR |
NR |
NR |
19.4 |
NR |
NR |
NR |
Ticks/Fleas infestation |
30 |
11 |
0 |
20 |
51.6 |
41.7 |
0 |
28.6 |
Helminthes |
73.3 |
100 |
100 |
0 |
38.7 |
75 |
44.4 |
42.9 |
Trypanosomiasis |
1.6 |
NR |
NR |
NR |
9.8 |
NR |
NR |
NR |
Swine fever |
NR |
NR |
0 |
NR |
NR |
NR |
100 |
NR |
Newcastle disease |
NR |
NR |
NR |
80 |
NR |
NR |
NR |
71.4 |
Coccidiosis |
NR |
NR |
NR |
10 |
NR |
NR |
NR |
8.3 |
Note: percentages are based on respondents, NR: Not relevant in the species |
Farmers reported various challenges they face in livestock. Major challenges that affected the different livestock species in the two districts were dry season feed shortages and livestock diseases (Table 4). Farmers reported strategies devised to meet some of the challenges like use of crop residues and non-conventional feeds like pineapple wastes as well as use of herbal concoctions as remedies for livestock pests and diseases. High prevalence of endemic diseases and lack of knowledge were sighted as the main challenges that hindered farmers from adopting organic animal husbandry practices in both districts.
Table 4: Challenges experienced by organic farmers in relation to the different livestock species |
||||||||
|
Number of respondents (%) |
|||||||
Kayunga district |
Luwero district |
|||||||
Cattle |
Goats |
Pigs |
Chicken |
Cattle |
Goats |
Pigs |
Chicken |
|
No farmers responded |
26 |
14 |
14 |
11 |
29 |
16 |
9 |
23 |
Challenges |
|
|
|
|
|
|
|
|
Dry season feed shortage |
14(53.8)* |
10(71.4) |
7(50) |
3(27.3) |
10(34.5) |
8(50) |
7(77.8) |
3(13.0) |
Shortage of water |
0 |
0 |
0 |
0 |
1(3.45) |
0 |
0 |
1(4.35) |
Land shortage |
3(11.5) |
0 |
0 |
0 |
3(10.3) |
0 |
0 |
0 |
Expensive labour |
2(7.69) |
0 |
0 |
0 |
1(3.45) |
0 |
0 |
3(13.0) |
Lack of equipment |
0 |
1(7.14) |
0 |
1(9.10) |
0 |
0 |
0 |
0 |
Limited market |
0 |
0 |
0 |
1(9.10) |
2(6.89) |
0 |
0 |
11(47.8) |
Low milk prices |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
High cost purchased feed |
0 |
2(14.3) |
6(42.8) |
6(54.5) |
1(3.45) |
1(6.25) |
0 |
5(21.7) |
Livestock diseases |
7(26.9) |
2(14.3) |
3(21.4) |
9(81.8) |
7(24.1) |
6(37.5) |
2(22.2) |
20(86.9) |
Theft |
1(3.84) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
(53.8)a Figures in parentheses represent the percentage of farmers mentioning that particular challenge, |
Several issues related to land availability came out of the results including land sizes in relation to the number of animals, land ownership, land fragmentation and prioritization of land use. This study revealed that smallholder organic farmers had an average of 5- 10 acres. The total land size was higher in Luwero than in Kayunga district. Land availability is central in determining the potential for organic livestock production since outdoor access is a requirement under organic animal husbandry (IFOAM 2000). The majority of farmers in the study area owned the land which probably enhanced their decision making on land use. Ownership to land provides security for long term investments like livestock production. Land fragmentation and prioritization of this land towards crop production, mainly pineapples, seemed to indicate a reduction in land available for livestock grazing. Such continued reduction in land might lead to limited outdoor access for the animals (Udo et al 2011). This would probably compromise animal health and welfare which are crucial aspects in organic animal farming.
Organic farms had a high level of diversity of livestock, crops and vegetation. The most important reason reported for diversification among smallholder farmers include averting risk in case of crop failure and animals acting as cash banks (Prein 2002). The diversification of flora and fauna seen among organic farmers can be the basis of a well-balanced system, allowing integration for nutrient recycling and effective resource use (Zake et al 2010). Cattle are particularly capable of this with their capacity to collect, transport, convert and deposit nutrients, thereby improving nutrient management in resource scarce farming systems (Mubiru 2008). Various studies have been done in Uganda on the benefits of nutrient recycling on smallholder farms (Walaga et al 2000; Esilaba et al 2005; Mubiru 2008).
The predominant animal breeds in the study area were found to be indigenous but some farmers opted to cross breed, particularly the dairy cattle as a way of improving milk production. Tropical breeds are known to have unique and outstanding characteristics such as adaptability to hot environment and resistance to endemic diseases; their low productivity not withstanding (Olawuni 2013). The use of well-adapted breeds is one of the major characteristics given much emphasis in organic production systems. therefore, disease prevention should preferably be based on animal breed adaptability and diversity of flora and fauna (Magnusson 2001; Stockdale et al 2001). For example, among the local breeds of free range cattle in Uganda, it is common to see either the egret birds or the oxpeckers picking ticks from cattle. Similarly it is a common practice for farmers to use local herbal remedies such as Phytolacca dodecandra or Tephrosia spp. to control ticks. This scenario of high prevalence of livestock diseases and pests under humid and high temperatures of the tropics can only be tolerated by indigenous breed. Therefore, infrastructural development, research and improving farmer’s knowledge on how to select for particular production traits from indigenous livestock based on organic farming principles under tropical conditions are suggested strategies that might support integrated smallholder organic pineapple production
Natural pastures were found to be the most common feed resource for ruminants in the area. Heavy dependence on natural pastures with limited avenues for conservation and animal supplementation characterized free range and tethering management practices by smallholder farmers. Since free range and tethering are communal in practice with animals being moved from one place to the other. This might also facilitate spread of diseases and pests. These practices challenge the health situation on the farms which probably explains why disease and feeds came out as the biggest challenges in the study area. The availability of natural pastures is dependent on availability of rainfall, therefore during the dry seasons there is always drastic scarcity of this resource. In addition, nitrogen is a limiting nutrient in many tropical pastures (Bogale et al 2008). From this study it is seen that farmers have small sizes of land, mainly dedicated to crop production, which implies that availability of land for sufficient animal grazing is a limiting factor for adequate animal feeding which might result in compromised immunity of animals, thus increasing their risk to diseases (Zollitsch et al 2004). Farmers have mitigated this challenge by either using crop residues as supplements to grazing pastures or adopting an intensification system, where cross-bred dairy cattle under stall feeding are fed on improved fodder such as elephant grass and fodder legumes such as Calliandra and Gliricidia. . The use of crop residues in the study area has been possible because as the dry season approaches, harvesting of crops like pineapples and maize are at the peak, providing an available resource that farmers can opt to use as animal feed or as compost. In addition, some farmers used fodder trees as animal feed, however the core purpose for such trees was to act as hedge to prevent soil erosion or provide shade. Studies have indicated that animals with access to fodder trees have shown better performance than those kept on natural pastures in terms of milk yield, weight gain, reproduction performance and survival rates (Norton 1994; Elbasha et al 1999).
The common management system among smallholder organic farmers was found to be tethering and free-range. This is consistent with results of earlier studies among other smallholder farmers in Uganda (Lubwama 2002; Kirunda and Mukiibi-Muka 2006; Byarugaba 2007). These management systems provide animals with sufficient outdoor access as required by the organic livestock standards (IFOAM 2000). Although tethering and free-range systems provide outdoor access, a requirement in the organic standards and desirable practices in organic animal husbandry, it increases the risk of animals coming into contact with a broad range of environmental pathogens which might comprise animal health (Kijlstra and Eijck 2006).
It is also likely that tethering impairs animal welfare which is contrary to organic values. Collectively, the two types of management system face future challenges of reduced grazing land as a result of farmers opening up more land for cultivation of organic pineapples that have higher economic returns. Therefore, there is need for strategies to intensify livestock production under organic farming systems.
The majority of farmers kept their animals under tree shades which act as ‘night kraals’, with a few farmers having sheds mainly for dairy animals. Animal housing serves several purposes, like to maintain animals in good health and keeping them tidy. Maintenance of health and welfare is a major objective of organic animal production (Hovi et al 2003; Vaarst and Alrøe 2011). Moreover, appropriate housing should address the behavioral need of the animals, paying attention to aspects including floor characteristics, locomotion area, stocking rates, and husbandry practices (Sundrum 2001). The absence of appropriate housing would increase animal stress that may render animals more susceptible to reduced immunity.
The absence of control over manure on smallholder organic farms results into loss of this vital resource, much of which is lost while animals are grazing in fields and roadsides. The manure that is available in ‘night kraals’, though reported to be used as fertilizer in crops, often runs off when it rains. One of the benefits of animals in an integrated system is to provide manure important for nutrient cycling (Zake et al 2010, Mubiru et al 2011). However, this benefit can be amassed if animal housing is considered as one of the essential farm structures. The limitation organic farmers currently face is lack of funds to invest into infrastructural development. Similarly, their livestock productivity is still minimal and not yet developed. Smallholder organic farmers are faced with a dilemma of whether to house animals indoors for purposes of accumulating manure for crop production or give them outdoor access for welfare reasons. A solution to this dilemma faced by the smallholder organic farmers could be to allow animals access to free range area during the day and bring them into sheds or night kraals overnight, which would allow collecting roughly half of the manure they excrete. This kind of management strategy is recommended since it can enable farmers to address manure access and animal welfare which are both important in organic farming.
This study revealed that helminths were the most common health concern on organic farms. These results are consistent with other studies which reported high prevalence of helminths under organic/ free range systems (Permin et al 1999; Lindqvist et al 2001; Carstensen et al 2002; Phiri et al 2007; Mukaratirwa and Khumalo 2010; Obonyo et al 2012). Ticks were another threat to ruminants, especially cattle. There were many cases of tick bites reported in Luwero district, yet more cases of East Coast Fever were registered in herds in Kayunga district. The high prevalence of ticks in Luwero district were possibly due to the management system which involved outdoor grazing that exposed animals to ticks on the pastures. However, since local breeds with better resistance to tick borne diseases were predominant, this reduced the occurrence of ECF. The reports on tick infestation in Kayunga district were low, probably because many farmers managed their cattle under zero grazing systems. However, the high occurrence of ECF reported was probably due to presence of cross-breeds with less resistance which were predominant under the zero grazing system. This demonstrates that it is probably not only land use that might deter farmers from having their herds outdoors, but also the disease and breed interaction. Findings in this study are similar to other studies which revealed that tick borne diseases are a major challenge for livestock production in the tropics (Vaarst et al 2006; Nalubwama et al 2011; Reye et al 2012) and a cause of mortality in calves among East African indigenous cattle (Homewood et al 2006).
Parasite infestation might result into infection depending on the infectious load, the nutritional and immune status of the animals (Kijlstra and Eijck 2006). Studies have developed parasite control measures including biological control of helminths, using certain strains of fungi such as Duddingtonia flagrans, frequent rotation, lower stocking rates or alternate grazing with other species (Thamsborg 2001). These strategies might also be useful in organic farms where reliance on synthetic veterinary drugs is regarded as an unsustainable strategy. Further research and development in practice is needed on the implementation, functioning and reliability of these concepts under the condition of organic farming in central Uganda.
Organic pineapple farmers mostly used synthetic veterinary drugs to manage livestock disease in the two districts with a few exceptions where herbal concoctions were used mainly to treat some infections in chicken. Similar results were reported by studies done in Uganda (Vaarst et al 2006; Vaarst et al 2008). Existing indigenous knowledge might also provide prospects for developing alternative remedies for animal diseases and pests under organic farming.
Livestock diseases and feed were the main challenges for livestock production among the organic pineapple farmers. These results are in agreement with studies already done by other researchers which indicated high prevalence of endemic diseases and inadequate feeds in tropical regions (Vaarst et al 2006; Bogale et al 2008; Vaarst et al 2008; Nalubwama et al 2011). Farmers also reported limited knowledge in organic animal farming which probably explains their continued use of conventional practices in managing livestock diseases. Moreover, farmers perceived the use of synthetic remedies as a more expensive and unsustainable approach to livestock production yielding no impressive solution to pests and disease management. There is therefore a desperate need for development of functioning organic alternatives that are cheaper and effective in the pest and disease control in this hot and humid environment.
Although lack of organic feeds may not be of great priority for farmers in the study area, since they do not practice organic livestock farming, lack of feeds in general and particularly in dry seasons causes a big challenge to livestock production in the tropics (Bogale et al 2008; Vaarst et al 2008). This mainly results from over reliance on natural pastures coupled with limited supplementation of ruminants as seen in this study. On the other hand, pig and poultry production is heavily dependent on supply of high protein level diets which are limited in many organic systems. The solution might be in feeding of high protein cereals; however these are competed for as food for humans. In conventional systems, provision of supplementary synthetic feed additives might be a solution but this is not acceptable in organic farming (IFOAM 2000). Further research and development in organic feeds is therefore needed to deal with nutritional challenges in organic farming systems.
Although there is some level of integration of livestock with organic pineapple production as evidenced by use of animal manure to fertilize pineapple fields and pineapple wastes as feed for animals, nutrient recycling was observed to be low for a majority of farms. Ironically, even in Kayunga district with more zero grazing units and with better possibilities of obtaining manure, most farmers did not use manure in pineapple production, probably because they depended on coffee husks as was observed on many farms. In Luwero district, where animals are either on free range or tethered, they dropped much of the manure on grazing grounds and therefore farmers were not able to gather it for recycling in pineapple gardens. Farmers are only able to utilize manure that remains in ‘night kraals’ but priority is given to bananas and coffee plantations and to a lesser extent to pineapple gardens. Possibly the high variability in nitrogen (5±1.5) and phosphorus (3±1.5) content of solid cattle manure as shown in many studies (Murwira et al 1995; Reynolds and De Leeuw 1995; Madiagne et al 1999; Rufino et al 2006) make the natural soil amendement an undependable source of plant nutrients . Failure to optimally use manure can also be attributed to inadequate volumes required for pineapple production (5 to 10 tonnes per hectare) due to small herd sizes, fear of weed disposal and introducing pests in the pineapple fields plus lack of appropriate infrastructure and equipment for manure collection, management and handling (Baltenweck et al 2007; Zake et al 2010). It was observed that farmers in Luwero district mostly cultivated pineapples mainly on previously fallowed land unlike in Kayunga district where such land is not available due to higher population density. Since land under fallow is normally fertile, there is less need to use manure or coffee husks in pineapple production in Luwero district. Farmers are also challenged with having non-organic livestock enterprise with certified pineapples located on the same piece of land.
Farmers reported feeding livestock with pineapple wastes including crowns, peels and the pith which are palatable to the animals. This is probably because pineapples contain large quantities of sugars but relatively little fibre. The leaves and skin of the fruit have also been used in Asia as anthelmintic preparations for livestock (Jovellanos 1997; Baldo 2001). However, the increased use of pineapple wastes as feed for livestock on organic pineapple farms has been limited by lack of sufficient knowledge of ways to transform such residues into a form with a longer shelf life. On the other hand, large volumes of organic pineapple wastes are accumulated at processing centers which are far from the farms, thus creating an additional challenge of transportation from the processing centers to the farms. These challenges have limited full integration of livestock into organic pineapple production among smallholder farmers. Other studies have also indicated the benefits and complexities of smallholder integrated crop-livestock systems (Alice 1999; Thornton and Herrero 2001; Zake et al 2010; Mubiru et al 2011).
Although organic farming requires that the whole farming system should be operated following strict organic farming principles, this holistic concept is not implemented on the farms studied herein: Farms in the study area practice livestock production which is not certified as organic and animals are majorly not kept in accordance with the organic principles under the same production unit with certified organic pineapple production which presents a dilemma of whether the two forms of agricultural production can be integrated. The smallholder farms were found to be diversified with various animals and several crops, making it a good basis for developing an integrated and sustainable system. Although there was indication of nutrient flows between animals and pineapples on the farms, manure was not the main source of fertilizer for organic pineapples. In addition, farmers were not fully utilizing pineapple products in livestock production. Integration of livestock and organic pineapple production can be developed further by tackling the specific challenges of infrastructural development, research and improving farmer’s knowledge on livestock production based on organic farming principles under tropical conditions. In addition, a move towards having organic pineapple farms in Uganda orientated towards organic livestock production will enable farmers to benefit from a fully integrated system for improving soil fertility and production of quality organic animal products for markets and home consumption.
The authors are grateful to the Danish Agency for International Development DANIDA for its financial support to the project, Productivity and Growth in Organic Value Chains (ProGroV) which funded this study. We are also grateful to Gidi Smolders from orgANIMprove NL for reviews provided during data analysis.
Alice P N 1999 Integrated crop-livestock management systems in sub saharan Africa. Environment , Development and Sustainability 1, 337-348.
Badgley C, Moghtader J, Quintero E, Zakem E, Chappell M J, Aviles-Vazquez K, Samulon A and Perfecto I 2007 Organic Agriculture and Global Food Supply. Renewable Agriculture and Food Systems 22, 86-108
Baldo R C 2001 Comparative efficacy of pineapple (Ananas comosus) leaves bolus and albendazole against gastrointestinal nematods in sheep PhD Thesis, University of the Phillipines, Los Banos, Phillipines.
Baltenweck I, Mubiru S, Nanyeenya W, Njoroge L, Halberg N, Romney D and Staal S 2007 Dairy farming in Uganda: Production Efficiency and Soil Management Strategies under Different Farming Systems. ILRI Research Report. International Livestock Research Institute, Nairobi, Kenya.
Bogale S, Melaku S and Yami A 2008 Matching livestock systems with available feed resources in the Bale highlands of Ethiopia. Outlook Agriculture 37, 105–110
Bolwig S, Gibbon P and Jones S 2009 The Economics of Smallholder Organic Contract Farming inTropical Africa. World Development 37, 1094-1104
Broom A 2005 Using qualiative interviews in CAM research: A guide to study design, data collection and data analysis. Complementary Therapies in Medicine 13, 65-73
Byarugaba D K 2007 The structure and importance of the commercial and village based poultry industry in Uganda. Poultry Sector country review, Unpublished.
Carstensen L, Vaarst M and Roepstorff A 2002 Helminth infection in Danish Organic Swine Herds. Veterinary Parasitology 106, 253-264
Elbasha E, Thornton Pand Tarawali G 1999 An Ex-Post Economic Impact Assessment of Planted Forages in West Africa. International Livestock Research Institute, Nairobi, Kenya.
Esilaba A O, Nyenda P, Nalukenge G, Byalebeke J B, Delve R J and Ssali H 2005 Resource flows and nutrient balances for crop and anaimal production in smallholder farming systems in Eastern Uganda. Agriculture, Ecosystems and Environment 109, 192-201
Gill P, Stewart K, Treasure E and Chadwick B, 2008 Methods of data collection in qualitative research: interviews and focus groups. British Dental Journal 204, 291-295
Halberg N, Rosegrant P, Sulser T, Knudsen MT and Hogh-Jensen H 2006 The impact of Organic farming on food security in regional and global perspective. In: Halberg N, Knudsen M T, Alrøe HF and Kristensen E S (Eds.), Global Development of Organic Agriculture: Challenges and Prospects. CABI Publishing, Wallingford, UK.
Herrero M, Thornton P K, Gerber P and Reid R S 2009a Livestock, Livelihoods and the Environment: understanding the trade offs. Current opinions on Evironmental Sustainability 1, 111-120
Herrero M, Thornton P K, Notenbaert A M, Msangi S, Freeman H, Bossio D, Dixon J, Peters M, Van de Steef J, Lynam J, Parthasarathy Rao P, Macmillian S, Gerard B, McDermott J J, Sere C and Rosegrant M 2010 Smart Investments in sustainable food production: revisiting mixed crop-livestock systems. Science 377, 822-825
Herrero M, Thornton P K., Notenbaert A, Wood S, Kruska R, Dixon J, Bossio D, Freeman H X L and Rao P 2009b Drivers of change in crop-livestock systems and their potential impacts on agroecosystems services and human welbeing to 2030. Livestock Research Institute, Nairobi, Kenya.
Homewood K, Trench P, Randall S, Lynen G and Bishop B 2006 Livestock health and socioeconomic impacts of a veterinary intervention in Maasailand: infection and treatment vaccine against East Coast Fever. Agicultural Systems 89, 248-271
Hovi M, Sundrum A andThamsborg S M 2003 Animal health and welfare in organic livestock production in Europe: Current state and future challenges. Livestock Prod.uction Science 80, 41-53
IAASTD, 2009 The International Assessement of Agricultural Science and Technology for Development. Island Press, Washington DC.
IFOAM 2000 Basic standard for organic production and processing. In: International Federation of Organic Agriculture Movement GA (Ed.), Basel.
Jovellanos J M M 1997 Efficacy of three selected herbal plants on gastrointestional parasites of cattle, PhD Thesis, University of the Philipines, Los Banos, Philipines.
Kijlstra A and Eijck I A J M 2006 Animal Health in organic livestock production systems: a review. Journal of Animal Science 54
Kirunda H and Mukiibi-Muka G 2006 Causes of chicken mortality in free range poultry in Busede subcounty, Jinja District. Livestock Systems Research Program Annual Scientific Workshop, Kampala.
Lindqvist A, Ljungstrom B N O and Waller P J 2001 The dynamics, prevalence and impact of nematode parasite infection in organically raised sheep in Sweden. Acta Veterinaria Scandinavica 42, 377-389
Lubwama J 2002 A survey of helminth infections in rural scavening chicken slaughtered in Kampala city markets. Undergraduate Thesis, Makerere University.
Madiagne D, Mankeur F and Yamoah C F 1999 Manure and Seasonal rainfall effects on millet and groundnut yields in semi-arid region of Senegal. African Crop Science Journal 7, 185-193
Magnusson U 2001 Breeding for disease resistance in organic farming- possibilities and constraints. Acta Veterinaria Scandinavica, Supplementum 95, 59-61
McDermott J J, Staal S J, Freeman H A, Herrero M and Van de Steef J A 2010 Sustaining intensification of smallholder livestock systems in the tropics. Livestock Science 130, 95-109
Mubiru LS 2008 Development of Nutrient Management Strategies Along a Continuum of Dairy Production intensification in Uganda, PhD Thesis, Faculty of Agriculture. Makererere University.
Mubiru LS, Ronmey D, Halberg N and Tenywa JS 2011 Development of nutrient management strategies based on mapping of Uganda nitrogen flows and balances in dairy production systems in Uganda. Livestock Science 137, 116-123
Mukaratirwa S and Khumalo M P 2010 Prevalance of helminth parasites in free-range chickens from selected communities in Kwazulu-Natal province of South Africa. J S Afr Assoc. 81, 97-101 Retrived March 27, 2014 from http://www.scielo.org.za/scielo.php?pid
Murwira H K., Swift M J and Frost P G H 1995 Manure as a key resource in sustainable agriculture: a case study of communal areas farming systems in Zimbabwe. In: Powell J M, Fernandez-Rivera S, William T O and Renard C (Eds.), Livestock and Sustainable Nutrient Cycling in Farming Systems of Sub-Saharan Africa, ILCA proceedings , Addis Ababa, Ethiopia, Pp. 131-148
Nalubwama S M, Mugisha A and Vaarst M 2011 Organic livestock production in Uganda: Potentials, Challenges and Prospects. Tropical Animal Health and Production 4, 749
Norton BW 1994 Tree legumes as dietary supplements for ruminants. In: Gutteridge R C and Shelton H M (Eds.), Forage Tree Legumes in Tropical Agriculture. CAB International, Wallingford, UK, pp. 192–201
Obonyo F O, Maingi N, Githigia S M and Ng'ang'a C J 2012 Prevalence, Intensity and Spectrum of helminths of free range pigs in Homabay District, Kenya. Livestock Research for Rural Development 24 (3)
Olawuni S 2013Tropical Dairy Breeds: Potentials,Problems and Productivity. LAP Lambert Academic Publishing, United Kingdom.
Permin A, Bisgaard M, Frandsen F, Pearman M, Kold J and Nansen P1999 Prevalence of gastrointestinal helminths in different poulty production systems. British Poultry Science 40, 439-443
Phiri I K, Phiri A M, Ziela M, Chota A, Masuku M and Monrad J 2007 Prevalence and distribution of gastrointestinal helminths and their effects on weight gain in free- range chickens in Central Zambia. Tropical Animal Health and Production 39, 309-315
Prein M 2002 Integration of aquaculture into crop-livestock animal systems in Asia. Agricultural Systems 71, 127-147
Reye A L, Olatunbosun G A, Hübschena J M and Mullera C P 2012 Pathogen Prevalence in Ticks Collected from Vegetion and Livestock in Nigeria. Applied Environmental Microbiology 78, 2562-2568
Reynolds L and De Leeuw P N 1995 Myth and manure in nitrogen cycling: A case study of Kaloleni Division in Coast Province, Kenya. In: Powell J.M, Fernandez-Rivera S, WilliamT O and Renalrd C (Eds.), Livestock and Sustainable Nutrient Cycling in Farming Systems of Sub- Saharan Africa, ILCA Proceedings, Addis Ababa, Ethiopia, pp. 509-521
Rufino M C, Rowe E C, Delve J and Giller K E 2006 Nitrogen cycling efficiencies through resource- poor African crop- livestock systems. Agriculture, Ecosystems and Environment 112, 261-282
Stockdale E A, Lampkin N H, Hovi M, Keatinge R, Lennartsson E K M, Macdonald D W, Padel S, Tattersall F H, Wolfe M S and Watson C A 2001 Agronomic and Environmental implications of organic farming systems. Advances in Agronomy 70, 261-325
Sundrum A 2001 Organic livestock farming: A crtitical Review. Livestock Production Sci ence 67, 297-215
Thamsborg S M 2001 Organic farming in the Nordic countries- Animal Health and Production. Acta veterinaria Scandinavica, Supplementum 95, 51-57
Thornton P K and HerreroM 2001 Integrated crop–livestock simulation models for scenario analysis and impact assessment. . Agricultural Systems 70, 581–602
UBOS 2012 Statisitical Abstract 2012. Uganda Beaurau of Statistics Retrived on December 5 , 2012 from http://www.ubos.org/onlinefiles/uploads/ubos/pdf%20documents/2012StatisticalAbstract.pdf
Udo H M J, Aklilu H A, Phong LT, Bosma R H, Budisatria I G S, Patil B R, Samdup T and Bebe B O 2011 Impact of intensification of different types of livestock production in smallholder crop-livestock systems. Livestock Science 139, 22-29
UEPB 2005 Product profile on Pineapple No.3. Uganda Export Promotion Board
UNPP 2008 Population Division of the Department of Economic and Social Affairs of the United Nations Secretariat, World Population Prospects: The 2006 Revision and World Urbanisation Prospects: The 2005 Revisions
Vaarst M and Alrøe H F 2011 Concepts of Animal Health and Welfare in Organic Livestock Systems. Journal of Agriculture and Environmental Ethics 25 (3), 333-347
Vaarst M Padel S, Younie D, Hovi M, Sundrum A and Rymer C 2008 Animal Health Challenges and Veterinary Aspects in Organic Farming Identified Through a 3 Year EU Network Project. The Open Veterinary Sciences 2
Vaarst M, Roderick S, Byarugaba D K, Kobayash I S, Rubaire-Akiiki C and Karreman H J 2006 Sustainable veterinary medical practices in organic farming: A global perspective. In: Halberg N, Alrøe HF, Knudsen MT, Kristensen E S (Eds.), Global Development of Organic Agriculture, Challenges {Vaarst, 2006 #92}and Prospects. CABI Publishing, pp. 241-276
Walaga C, Egulu B, Bekunda M and Ebanyat P 2000 Impact of policy change on soil fertility management in Uganda. In: Hilhorst T and Muchena F(Eds.), Nutrients on the Move. Soil fertility dynamnics in African farming systems, pp. 29-44
Wright I, Tarawali S, Blummel M, Gerard B, Teufel N and Herrero M 2011 Integrating crop and livestock in subtropical agricultural systems. Journal of the Science of Food and Agriculture 92(5)
Zake J, Tenywa J S and Kabi F 2010 Improvement of Manure Management for Crop Production in Central Uganda. Journal of Sustainable Agriculture 34, 595-617
Zollitsch W, Kristensen T, Krutzinna C, MacNaeihde F and Younie D 2004 Feeding for Health and Welfare: The Challenge of Formulating Well-balanced Rations in Organic Livestock Production. In: Vaarst M, Roderick S, Lund V and Lockeretz W (Eds.), Animal Health and Welfare in Organic Agriculture. CAB International, p. 329
Received 25 March 2014; Accepted 18 April 2014; Published 1 June 2014