<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AS</journal-id><journal-title-group><journal-title>Agricultural Sciences</journal-title></journal-title-group><issn pub-type="epub">2156-8553</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/as.2023.1411101</article-id><article-id pub-id-type="publisher-id">AS-129165</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject><subject> Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Utilisation of Non-Conventional Animal Waste as Feeds by Multiple Livestock Species Farmers in Lake Victoria Crescent of Central Uganda
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Stephen</surname><given-names>Kabugo</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Samuel</surname><given-names>Okello</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Sarah</surname><given-names>A. Nalule</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>David</surname><given-names>Kahwa</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Department of Agricultural Production, Kyambogo University, Kyambogo, Uganda</addr-line></aff><aff id="aff3"><addr-line>Department of Wild Life and Aquatic Resources, School of Veterinary Medicine and Animal Resources, College of Veterinary Medicine, Animal Resources and Biosecurity, Makerere University, Kampala, Uganda</addr-line></aff><aff id="aff2"><addr-line>Department of Livestock and Industrial Resources, School of Veterinary Medicine and Animal Resources, College of Veterinary Medicine, Animal Resources and Biosecurity, Makerere University, Kampala, Uganda</addr-line></aff><pub-date pub-type="epub"><day>08</day><month>11</month><year>2023</year></pub-date><volume>14</volume><issue>11</issue><fpage>1561</fpage><lpage>1572</lpage><history><date date-type="received"><day>8,</day>	<month>October</month>	<year>2023</year></date><date date-type="rev-recd"><day>18,</day>	<month>November</month>	<year>2023</year>	</date><date date-type="accepted"><day>21,</day>	<month>November</month>	<year>2023</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution-NonCommercial International License (CC BY-NC).http://creativecommons.org/licenses/by-nc/4.0/</license-p></license></permissions><abstract><p>
 
 
  A cross-sectional survey was conducted to establish the utilisation of non-conventional animal waste in multiple livestock species systems. Farmers (150) were selected from four out of ten districts of Central Uganda in Lake Victoria Crescent. A structured questionnaire was used and descriptive analysis showed that over 80% are smallholder farmers on &lt;1.0 Ha of land practice mixed livestock combinations. Farmers (16%) are shifting to integrated livestock species combinations with the acquisition of faming experience (&gt;3.0) years. Household husbands (80%) significantly (P &lt; 0.001) influence choices of livestock and production systems. Labour is majorly family (40.7%) with house wives (63.3%) actively involved in farm operations. Farmers (86.3%) use costly conventional feeds which influence (P &lt; 0.001) livestock categories and production efficiency. Farmers (16.7%) are shifting to cheaper and readily available non-conventional feeds with over 50% using swills ranked I (RI) for its availability, nutritious and cheap followed by blood (RII) and bone meal (RII). Others in RII are meat offal, fish meal, insect meal and rumen offal. In RIII are dead chicks, hatchery rejects and animal litter. In RIV are oyster shells while bio-yeast and insect-maggot-worm are in RV which are the most costly and unavailable feeds. Maggot and worm feed are cheaply cultured from poultry faeces (52%) and cattle dung (25%) for mainly fish and monogastric production. Untreated non-conventional feeds are relatively risky (RR &gt; 1.0) as they cause poor livestock health due to pathogens, parasites and toxins which are associated (OD &gt; 1.0) with poor growth, mortality and condemnation of livestock products. The remedy to unsafe non-conventional feeds is to apply effective solar-heating (75%), chemical and ensiling treatment methods. The study showed that there are no significant (P &lt; 0.001) public health risks associated with utilising treated non-conventional feeds instead it improves production and sustainability of multiple livestock species systems.
 
</p></abstract><kwd-group><kwd>Multiple Livestock Species</kwd><kwd> Non-Conventional Feed</kwd><kwd> Animal Waste</kwd><kwd> Public Health</kwd><kwd> Feed Treatment</kwd><kwd> Central Uganda</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>The demand for animal products in Lake Victoria Crescent including Central Uganda is expected to increase beyond 70% by 2050 which requires coping strategies for sustainable livestock production systems for food security. As a matter of public concern and scientific remedy, population dynamics, climatic and ecological situation need interventional measures (Bern&#232;s et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref1">1</xref>] ). Livestock farming demands enormous resources, feeds being the most challenging due to limited availability of feed ingredients, climatic change and food-feed-fuel competition (Makkar et al., 2014 [<xref ref-type="bibr" rid="scirp.129165-ref2">2</xref>] ). As a guiding principle, the notion “waste” refers to a misplaced resource but can still be converted into valuable livestock inputs. The potential of animal waste as non-conventional feeds could be exploited through proper processing, recovery and recycling to feed livestock (Haobijam &amp; Souvik Ghosh, 2018 [<xref ref-type="bibr" rid="scirp.129165-ref3">3</xref>] ). Animal waste as feeds focuses on the nutritive value, levels of feeding, environment factors such as housing and health (M&#252;ller, 1982 [<xref ref-type="bibr" rid="scirp.129165-ref4">4</xref>] ; Flachowky, 1997 [<xref ref-type="bibr" rid="scirp.129165-ref5">5</xref>] ). The success of livestock production system depends on the feed conversion efficiency of animal waste into feed resources (Haobijam &amp; Souvik Ghosh, 2018 [<xref ref-type="bibr" rid="scirp.129165-ref3">3</xref>] ). In view of minimizing the use of costly conventional feeds, animal waste feeds should be exploited to improve livestock production and sustainability (Sikka, 2006) [<xref ref-type="bibr" rid="scirp.129165-ref6">6</xref>] ). Excretion and litter from livestock can be alternative basal feed, and substrate for culturing insects as feeds for livestock and fish (Nasiru et al., 2014 [<xref ref-type="bibr" rid="scirp.129165-ref7">7</xref>] . Animal waste feed including entomophagy in nutrient reuse can be a remedy to costly feeds in mixed and integrated livestock systems (Van Huis et al., 2015 [<xref ref-type="bibr" rid="scirp.129165-ref8">8</xref>] ). The presence of antimicrobial drugs, pesticides, mycotoxins and hormonal residues in feeds affects animal performance (Crawshaw, 2012 [<xref ref-type="bibr" rid="scirp.129165-ref9">9</xref>] ). The pathogen risks, and xenobiotic problems render animal waste feeds unsafe and lower animal products quality (Fink-Gremmels, 2012 [<xref ref-type="bibr" rid="scirp.129165-ref10">10</xref>] ). Consumption of products from waste-fed animals as envisaged from the health and safety standpoint requires processing and treatment technologies. Dehydration, ensiling, chemical and mechanical treatment are some of the effective methods used to process animal waste feeds to acceptable levels (McAllister et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref11">11</xref>] ; Chen, 2015 [<xref ref-type="bibr" rid="scirp.129165-ref12">12</xref>] ). Composting and biodegradation of waste via insect cultures or manure could also be used as recycling processes (Acu&#241;a et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref13">13</xref>] ; Peiretti et al., 2014 [<xref ref-type="bibr" rid="scirp.129165-ref14">14</xref>] ). Animal waste not only increases production but also is potentially useful for survival of animals during seasonal feed scarcity (Mwesigwa et al., 2020 [<xref ref-type="bibr" rid="scirp.129165-ref15">15</xref>] ). Proper processing of animal waste and nutrient balancing with other ingredients can potentially substitute 30% of conventional feeds without compromising the quality of livestock products (Tadele, 2015 [<xref ref-type="bibr" rid="scirp.129165-ref16">16</xref>] ). Supplementation or substitution of conventional feeds with non-conventional feeds can efficiently support feasible and sustainable livestock-fish production systems (Makkar and Ankers, 2014 [<xref ref-type="bibr" rid="scirp.129165-ref17">17</xref>] ; Komolafe and Sonaiya 2014) [<xref ref-type="bibr" rid="scirp.129165-ref18">18</xref>] ). The survey therefore, sought to ascertain the potential and safe utilization of processed non-conventional feeds for improvement and sustainability of multiple livestock species production in Lake Victoria Crescent of Uganda.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Study Area</title><p>A survey focused on multiple livestock species production and fishing districts in Lake Victoria Crescent (LVC) of Uganda (LVB, 2013 [<xref ref-type="bibr" rid="scirp.129165-ref19">19</xref>] ). The area receives total annual rainfall of 2400 mm with bimodal distribution and temperature range of 16˚C - 28.7˚C (MAAIF, 2011 [<xref ref-type="bibr" rid="scirp.129165-ref20">20</xref>] ). LVC consists of 10 districts with potential for sustainable livestock agriculture to cater for a population of 30 million of which 60% are unemployed and live below poverty line (UBOS, 2015 [<xref ref-type="bibr" rid="scirp.129165-ref21">21</xref>] ). A region with low livestock production due to costly conventional feeds accounts for 75% of expenses (Sikka, 2006) [<xref ref-type="bibr" rid="scirp.129165-ref6">6</xref>] ). Livestock product consumption is still constrained by socio-cultures and public health risks among the communities (LVBC, 2007 [<xref ref-type="bibr" rid="scirp.129165-ref22">22</xref>] ).</p></sec><sec id="s2_2"><title>2.2. Data Collection</title><p>Data on utilisation non-conventional feeds in multiple livestock species farmers was collected from 150 selected respondents for a period of three months from four districts of Buikwe, Kayunga, Mukono and Wakiso representing LVC of Central Uganda. The respondents were multiple livestock farmers rearing more than two livestock on the same farm and adopting animal waste feed resources in diets of animals and fish. Guided interview with a structured questionnaire was used to collect data as described by Broom, (2005) [<xref ref-type="bibr" rid="scirp.129165-ref23">23</xref>] and Gill et al., 2005 [<xref ref-type="bibr" rid="scirp.129165-ref24">24</xref>] ).</p></sec><sec id="s2_3"><title>2.3. Data Analysis</title><p>Data was coded and entered into the SPSS computer software (IBM SPSS statistics 20). Qualitative information gathered during the study was quantified and subjected to descriptive statistics at P &lt; 0.05 in form of percentages. Chi-square (X<sup>2</sup>) test was used to identify the most significant difference in risk factors associated with utilization of non-conventional feeds by multiple livestock species farmers in LVC of Central Uganda.</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Characterisation of Households</title><p>The results in <xref ref-type="table" rid="table1">Table 1</xref> shows that multiple livestock species systems (MLS) farmers (84%) practice predominantly mixed species combinations while 16% integrated species with inclusion of fish. MLS farmers (80%) in LVC are smallholders with less than one hectare of land (LVBC, 2007 [<xref ref-type="bibr" rid="scirp.129165-ref22">22</xref>] ). Livestock farming is male (80%) dominated by husbands but wives (20%) are involved more in farm activities. Farmers (78.8%) with experience of (&gt;3.0) years practice MLS more sustainably. Only 17% of the farmers are using less costly non-conventional feeds and more expensive traditional feeds by 83.3% of farmers. Income from livestock by-products remain low at 30 %, while 70% of the farmers earn income mainly</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Participant’s demographic characteristics and categories (n = 150) in LVC of Central Uganda</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Characteristic</th><th align="center" valign="middle" >Category</th><th align="center" valign="middle" >Frequency-n (%)</th></tr></thead><tr><td align="center" valign="middle" >Gender of farmers Experience (Years) Land size for livestock (ha) Labour Provision Family involvement Multiple livestock species Feed Household income</td><td align="center" valign="middle" >Males Female &lt;3.0 &gt;3.0 &lt;1.0 &gt;1.0 Family Hired Family and hired Male/Husband Female/wife Mixed C-F-G-Pi-Po* Integrated C-F-G-Pi-Po Conventional Non-conventional Animal products By-products</td><td align="center" valign="middle" >120 (80.0) 30 (20.0) 32 (21.3) 119 (78.7) 120 (80.0) 30 (20.0) 61 (40.7) 33 (22.0) 56 (37.3) 52 (34.7) 98 (65.3) 126 (84.0) 24 (16.0) 125 (83.3) 25 (16.7) 104 (69.3) 46 (30.7)</td></tr></tbody></table></table-wrap><p>* Po-Pi-G-F species combination: Ruminant (C = Cattle, G = goat/sheep), Monogastric (Pi = Pig, Po = Poultry), F = Fish.</p><p>from sale of livestock products in LVC (Acu&#241;a et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref13">13</xref>] ; Makkar et al., 2014 [<xref ref-type="bibr" rid="scirp.129165-ref2">2</xref>] ).</p></sec><sec id="s3_2"><title>3.2. Utilisation Non-Conventional Feeds in Livestock Production</title><p>The adoption and increased use of non-conventional feeds (NF) is enhanced by farmers’ ability to acquire occupational practice and experience (Komolafe and Sonaiya, 2014) [<xref ref-type="bibr" rid="scirp.129165-ref18">18</xref>] ). <xref ref-type="fig" rid="fig1">Figure 1</xref> shows that majority of the farmers (59.3%) acquire occupational practice and experience from other farmers, friendly interactions (22.2%), media and agro-companies (11.1%).</p><p>Efficient and economic use of NF should be in tandem with farming experiences and livestock performance (Smith and Wheeler, 1979 [<xref ref-type="bibr" rid="scirp.129165-ref25">25</xref>] ). <xref ref-type="fig" rid="fig2">Figure 2</xref> shows the methods for determining the right quantities of feed to avoid feed wastage, inadequate feeding and poor growth performance of livestock. Lack of measuring equipment renders the farmers (70%) to estimation feeds. Only 25% of the farmers possess weighing scales for accurate measurement of feeds. Farmers (5%) apply trial and error or unrestricted feeding methods which cause</p><p>feed wastage, inadequate feeding and improper growth performance of livestock (M&#252;ller, 1982 [<xref ref-type="bibr" rid="scirp.129165-ref4">4</xref>] ).</p><p>The findings in <xref ref-type="table" rid="table2">Table 2</xref> indicate the types of NF commonly utilised by farmers as indicated by Tadele (2015) [<xref ref-type="bibr" rid="scirp.129165-ref16">16</xref>] and ranking in MLS production. Swills are the highest ranked (RI) as they are readily availability, nutritious and low cost by 58% of farmers. Meat offal, fish meal, insect meal, bone, rumen offal and blood meal are in RII as most nutritious and low cost feed used by 50% of the farmers. Dead chicks, hatchery rejects, animal litter in RIII as the most available and nutritious. The most available and less costly are oyster shells in RIV. Bio-yeast and insect maggot and worm meal in RV are nutritious, not easily available and costly. Availability, cost and nutritional capacity of non-conventional feeds determine the quantities, livestock categories and systems to adopt by farmers (Makkar and Ankers, 2014 [<xref ref-type="bibr" rid="scirp.129165-ref17">17</xref>] ).</p></sec><sec id="s3_3"><title>3.3. Utilisation of Animal Waste as Substrate for Culturing Non-Conventional Feeds</title><p><xref ref-type="fig" rid="fig3">Figure 3</xref> shows the different animal waste substrates used for culturing insect worms and maggots as feeds in livestock production. Chicken faecal substrate is the most productive and used by 52% of the farmers, 25% prefer cattle dung to pig (10%) and goat or sheep dung (3%), and bio-slurry (4%) in production of worms for animal feeds. Some farmers (6 %) prefer faecal waste substrates from</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Types and ranking of non-conventional feeds utilised by farmers in LVC of Central Uganda.<sup> </sup></title></caption><table><tbody><thead><tr><th align="center" valign="middle"  colspan="3"  >Multiple livestock species farmers (n = 150)</th></tr></thead><tr><td align="center" valign="middle" >Nonconventional feeds</td><td align="center" valign="middle" >Utilisation n (%)*</td><td align="center" valign="middle" >Rank**</td></tr><tr><td align="center" valign="middle" >Food waste/swills Blood Bone/horn meal Animal litter Meaty/offal Oyster shells Rumen/gut content Dead chicks/rejects Insect meal Fish waste Bio-yeast Insects-maggot-worm meal Egg shells</td><td align="center" valign="middle" >88 (58) 82 (55) 79 (53) 60 (40) 47 (31) 15 (10) 13 (9) 12 (8) 12 (8) 5 (3) 3 (2) 2 (1) 2 (1)</td><td align="center" valign="middle" >I II II III II IV II III II II V V V</td></tr></tbody></table></table-wrap><p>*Respondents (n) in percentage (%), **Rank: I = Available, nutritious, low cost, II = Nutritious, low cost, III = Available, nutritious, IV = Available, Low cost, V = Nutritious, unavailable and costly.</p><p>other rare species such as rabbits to produce worms as livestock feeds (Acu&#241;a et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref13">13</xref>] ). <xref ref-type="fig" rid="fig4">Figure 4</xref>(a) indicates that livestock farmers are fast adopting to the use of less costly maggots and worms, which are cultured from different</p><p>animal faecal substrates. The insect feeds are fed to livestock species mainly fish and monogastric, namely pigs and poultry to substitute the scarce and costly conventional feeds such as fish meal (Van Huis et al., 2015 [<xref ref-type="bibr" rid="scirp.129165-ref8">8</xref>] ).</p><p>Farmers use more of the worms and maggots as nutritious feeds for fish. Poultry and pig farmers are using the same feed resources as either supplements or substitutes for conventional feeds (Sika, 2006 [<xref ref-type="bibr" rid="scirp.129165-ref6">6</xref>] ). Animal waste feeds from slaughter houses, hatcheries, swills and manure are being used mainly to feed fish. With more acquisition of feeding knowledge, the same feeds are being used for poultry and pigs (MacAllister et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref11">11</xref>] ). The findings in <xref ref-type="fig" rid="fig4">Figure 4</xref>(b) indicate that about 35% of the farmers feed pigs and fish on food and drink waste while 27% feed it to poultry. Slaughter waste is mainly used as feeds for fish by 54% of respondents, pigs by 33% and only 13% feed it to poultry (Mwesigwa et al., 2020 [<xref ref-type="bibr" rid="scirp.129165-ref26">26</xref>] ). The findings from the study established that 7% of the respondents do lack or have inadequate knowledge to utilize non-conventional feeds in multiple-species livestock production (Nasiru et al., 2014 [<xref ref-type="bibr" rid="scirp.129165-ref7">7</xref>] ). The findings from the study as shown in <xref ref-type="fig" rid="fig5">Figure 5</xref> established that majority of the respondents (42%) consider feed quality as a major factor in determining the type of non-conventional feeds to utilise, 25% consider animal stage, 13% on the animal type reared and feed adequacy while 7% do lack or have in adequate knowledge for the choice of non-conventional feeds to utilise in multiple livestock species production.</p></sec><sec id="s3_4"><title>3.4. Characteristic Variables of Non-Conventional Feeds on Livestock and Public Health Risks</title><p>The exposure of livestock to health risks, public health and negative social perceptions associated with the use of non-conventional feeds (NF), which affect acceptability of the consumer products are shown in <xref ref-type="table" rid="table3">Table 3</xref>.</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Effect of non-conventional feeds on livestock and public health</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Variable</th><th align="center" valign="middle"  colspan="8"  >Characteristic health effects of non-conventional feeds</th><th align="center" valign="middle" ></th></tr></thead><tr><td align="center" valign="middle" >Effect n (%)</td><td align="center" valign="middle" >No effect n (%)</td><td align="center" valign="middle" >Odds of effect</td><td align="center" valign="middle" >Risk of effect</td><td align="center" valign="middle" >OR</td><td align="center" valign="middle" >RR</td><td align="center" valign="middle" >X<sup>2</sup></td><td align="center" valign="middle" >P-value*</td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Micro/pathogen Exposed Not exposed Endo-parasites Exposed Not exposed Toxins Exposed Not exposed Growth Good Poor Mortality Low High Fear/perception Social risk Health risk</td><td align="center" valign="middle" >92 (61.3) 38 (25.3) 84 (56) 40 (27) 85 (56.7) 34 (23.0) 59 (39.3) 94 (62.7) 65 (43.3) 102 (68.0) 98 (65.3) 68 (45.3)</td><td align="center" valign="middle" >58 (38.7) 112 (74.7) 66 (44) 110 (73) 65 (43.3) 116 (77.0) 91(60.7) 56 (37.3) 85 (56.7) 48 (32.0) 52 (34.7) 82 (54.7)</td><td align="center" valign="middle" >1.59 0.34 1.27 0.36 1.89 0.27 0.68 2.59 0.78 2.13 1.88 0.83</td><td align="center" valign="middle" >0.61 0.25 0.56 0.27 0.65 0.21 0.39 0.59 0.43 0.68 0.65 6.45</td><td align="center" valign="middle" >4.68 3.50 7.00 0.39 0.36 2.27</td><td align="center" valign="middle" >2.42 2.1 3.08 0.63 0.64 1.44</td><td align="center" valign="middle" >39.5837 26.6129 36.2273 16.3399 18.4908 12.1381</td><td align="center" valign="middle"  colspan="2"  >0.00001 0.00001 0.00001 0.000053 0.000017 0.000494</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><p>*Significant at P &lt; 0.05, OR = Odds ratio RR = Risk ratio X<sup>2</sup> = Chi-square statistic value.</p><p>The findings show that it is risky (RR &gt; 1.0) to use untreated NF of animal origin due to presence of pathogens, endo-parasites and toxins. These are associated (OR &gt; 0.1) with poor growth and mortality of livestock. NF are rejected (OR &gt; 1.0) on basis of social perception than on associated health risk (RR &gt; 1.0) in livestock production. There is no significant (P &lt; 0.001) reason for rejection of treated NF as nonnutritive and unsafe for both livestock and public health (Fink-Gremmels, 2012 [<xref ref-type="bibr" rid="scirp.129165-ref10">10</xref>] ). Treated NF is safe for both livestock and human health, it is a precursor for development of livestock sector (Bern&#232;s et al., 2011 [<xref ref-type="bibr" rid="scirp.129165-ref1">1</xref>] ).</p></sec><sec id="s3_5"><title>3.5. Treatment and Preservation Methods of Non-Conventional Feeds</title><p>Non-conventional feeds should be treated and processed before use in order to improve their nutritional potential, increase safety and livestock product acceptability by consumers (Fink-Gremmels, 2012 [<xref ref-type="bibr" rid="scirp.129165-ref10">10</xref>] ). The different treatment and processing methods used by some of the farmers in Lake Victoria Crescent are as shown in <xref ref-type="fig" rid="fig6">Figure 6</xref>. The use of solar treatment and processing of NF was regarded as an effective method of improving shelf life, pathogen and toxin</p><p>control by 75% of respondents. Chemical treatment is effectively applied by 15% of respondents while 8% commend the feed ensiling treatment (Crawshaw, 2012 [<xref ref-type="bibr" rid="scirp.129165-ref9">9</xref>] ). Other 2% apply integrated treatments in processing and preservation of feeds. Treatment during processing methods is found to reduce health risks and improve healthy safety and acceptability of consumer products (Ogello et al., 2013) [<xref ref-type="bibr" rid="scirp.129165-ref27">27</xref>] .</p></sec></sec><sec id="s4"><title>4. Conclusion</title><p>The study established that there are bio-spherical and socio-economic setbacks facing multiple livestock species production in Lake Victoria Crescent. Poor and costly traditional feeds contribute greatly to low income and sustainability of livestock production. Utilisation of nutrients through recycling and non-conventional feeds of animal origin is a remedy to scarce and costly traditional feeds which cause low production. However, non-conventional feeds should be properly treated to avoid animal and public health incidences causing sickness and death. Effective treatment methods of feeds should be utilised to remove fears and negative social perception of consuming livestock products. The study emphasized safety, enhancement of consumer confidence and acceptability of livestock products. The future prospects of multiple livestock species systems lie in utilising cheap non-conventional feeds as a remedy to high cost of production and low output.</p></sec><sec id="s5"><title>Acknowledgments</title><p>The authors are grateful for the financial support from Makerere University and Swedish International Development Agency (MAK-SIDA) in collaboration with Kyambogo University. Highly appreciate the staff of Uganda National Farmers Federation (UNFFE) of Buikwe, Kayunga, Mukono and Wakiso districts. This work is Reference: SVARREC/05/2018 and National Council for Science and Technology, NCST A9ES.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s7"><title>Cite this paper</title><p>Kabugo, S., Okello, S., Nalule, S.A. and Kahwa, D. (2023) Utilisation of Non-Conventional Animal Waste as Feeds by Multiple Livestock Species Farmers in Lake Victoria Crescent of Central Uganda. Agricultural Sciences, 14, 1561-1572. https://doi.org/10.4236/as.2023.1411101</p></sec></body><back><ref-list><title>References</title><ref id="scirp.129165-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Bernués, A., Ruiz, R., Olaizola, A., Villalba, D. and Casasús, I. (2011) Sustainability of Pasture-Based Livestock Farming Systems in the European Mediterranean Context: Synergies and Trade-Offs. Livestock Science, 139, 44-57. https://doi.org/10.1016/j.livsci.2011.03.018</mixed-citation></ref><ref id="scirp.129165-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Makkar, H.P.S., Tran, G., Heuzé, V. and Ankers, P. (2014) State-of-the-Art on Use of Insects as Animal Feed. Animal Feed Science and Technology, 197, 1-33. https://doi.org/10.1016/j.anifeedsci.2014.07.008</mixed-citation></ref><ref id="scirp.129165-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Haobijam, J.W. and Ghosh, S. (2018) Integrated Pig-Fish Farming: A Case Study in Imphal West District of Manipur. The Pharma Innovation Journal, 7, 495-499.</mixed-citation></ref><ref id="scirp.129165-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Müller, Z.O. (1982) Feed from Animal Wastes, Feeding Manual. Food and Agriculture Organization of the United Nations, Roma.</mixed-citation></ref><ref id="scirp.129165-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Flachowsky, G. (1997) Animal Excreta as Feedstuff for Ruminants—A Review. Journal of Applied Animal Research, 12, 1-40. https://doi.org/10.1080/09712119.1997.9706185</mixed-citation></ref><ref id="scirp.129165-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Sikka, S.S. (2006) Effect of Incorporating Biogas Slurry (BGS) on the Growth Performance and Carcass Traits of Growing Pigs. Livestock Research for Rural Development, 18, No. 5.</mixed-citation></ref><ref id="scirp.129165-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Nasiru, A., Ibrahim, M.H. and Ismail, N. (2014) Nitrogen Losses in Ruminant Manure Management and Use of Cattle Manure Vermicast to Improve Forage Quality. International Journal of Recycling Organic Waste Agriculture, 3, Article No. 57. https://doi.org/10.1007/s40093-014-0057-z</mixed-citation></ref><ref id="scirp.129165-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Van Huis, A., Dicke, M. and Van Loon, J.J.A. (2015) Insects to Feed the World. Journal of Insects as Food and Feed, 1, 3-5. https://doi.org/10.3920/JIFF2015.x002</mixed-citation></ref><ref id="scirp.129165-ref9"><label>9</label><mixed-citation publication-type="book" xlink:type="simple">Crawshaw, R. (2012) Animal Feeds, Feeding Practices and Opportunities for Feed Contamination: An Introduction. In: Fink-Gremmels, J., Ed., Animal Feed Contamination, Woodhead Publishing Limited, Sawston, 11-32. https://doi.org/10.1533/9780857093615.11</mixed-citation></ref><ref id="scirp.129165-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Fink-Gremmels, J. (2012) Animal Feed Contamination: Effects on Livestock and food Safety. Woodhead Publishing, Sawston. https://doi.org/10.1016/B978-1-84569-725-9.50031-5</mixed-citation></ref><ref id="scirp.129165-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">McAllister, T.A., Beauchemin, K.A., Hao, X., McGinn, S.M. and Robinson, P.H. (2011) Greenhouse Gases in Animal Agriculture—Finding a Balance between Food Production and Emissions. Animal Feed Science and Technology, 166-167, 1-6. https://doi.org/10.1016/j.anifeedsci.2011.04.057</mixed-citation></ref><ref id="scirp.129165-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Chen, T., Jin, Y. and Shen, D. (2015) A Safety Analysis of Food Waste-Derived Animal Feeds From Three Typical Conversion Techniques in China. Waste Management, 45, 42-50. https://doi.org/10.1016/j.wasman.2015.06.041</mixed-citation></ref><ref id="scirp.129165-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Acu&amp;#241;a, A.M., Caso, L., Aliphat, M.M. and Vergara, C.F. (2011) Edible Insects as Part of the Traditional Food System of the Popoloca Town of Los Reyes Metzontla, Mexico. Journal of Ethnobiology, 31, 150-169. https://doi.org/10.2993/0278-0771-31.1.150</mixed-citation></ref><ref id="scirp.129165-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Peiretti, P.G., Tassone, S., Gai, F., Gasco, L. and Masoero, G. (2014) Rabbit Feces as Feed for Ruminants and as an Energy Source. Animals, 4, 755-766. https://doi.org/10.3390/ani4040755</mixed-citation></ref><ref id="scirp.129165-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Mwesigwa, R., Karubiu, P.M., King’ori, A.M. and Onjoro, P.A. (2020) Extent of Rumen Contents Use in Livestock Diets among Farmers in Uganda. African Journal of Agricultural Research, 15, 248-255. https://doi.org/10.5897/AJAR2019.14652</mixed-citation></ref><ref id="scirp.129165-ref16"><label>16</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Tadele</surname><given-names> Y. </given-names></name>,<etal>et al</etal>. (<year>2015</year>)<article-title>Utilization of Farm Animal Organic Waste as Feeds for Livestock and Poultry</article-title><source> Advances in Life Science and Technology</source><volume> 32</volume>,<fpage> 73</fpage>-<lpage>83</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.129165-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Makkar, H.P.S. and Ankers, P. (2014) Towards Sustainable Animal Diets: A Survey-Based Study. Animal Feed Science Technology, 198, 309-322. https://doi.org/10.1016/j.anifeedsci.2014.09.018</mixed-citation></ref><ref id="scirp.129165-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Komolafe, A.A. and Sonaiya, E.B. (2014) Simple Processing Methods for Recycling Poultry Waste into Animal Feed Ingredients. International Journal of Applied Agricultural and Apicultural Research, 10, 21-32.</mixed-citation></ref><ref id="scirp.129165-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">FAO (2019) Africa Sustainable Livestock 2050—Livestock Sector Development in Asia and Sub-Saharan Africa—A Comparison of Sector Growth and Transformation. Rome, 46 p. Licence: CC BY-NC-SA 3.0 IGO.</mixed-citation></ref><ref id="scirp.129165-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">MAAIF (2011) Statistical Abstract 2011, Entebbe, Uganda: Agricultural Planning Department, Ministry of Agriculture, Animal Industry and Fisheries (MAAIF).</mixed-citation></ref><ref id="scirp.129165-ref21"><label>21</label><mixed-citation publication-type="other" xlink:type="simple">UBOS (2015) Population Projections 2015-2020. https://www.ubos.org/population-projections</mixed-citation></ref><ref id="scirp.129165-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">LVBC: Lake Victoria Basin Commission (2007) Shared Vision and Strategy Framework for Management and Development of Lake Victoria Basin. Popular Version.</mixed-citation></ref><ref id="scirp.129165-ref23"><label>23</label><mixed-citation publication-type="other" xlink:type="simple">Broom, A. (2005) Using Qualitative Interviews in CAM Research: A Guide to Study Design, Data Collection and Data Analysis. Complementary Therapies in Medicine, 13, 65-73. https://doi.org/10.1016/j.ctim.2005.01.001</mixed-citation></ref><ref id="scirp.129165-ref24"><label>24</label><mixed-citation publication-type="other" xlink:type="simple">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. https://doi.org/10.1038/bdj.2008.192</mixed-citation></ref><ref id="scirp.129165-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Smith, L.W. and Wheeler, W.E. (1979) Nutritional and Economic Value of Animal Excreta. Journal of Animal Science, 48, 144-156. https://doi.org/10.2527/jas1979.481144x</mixed-citation></ref><ref id="scirp.129165-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Mwesigwa, R., Migwi, P.K., King’ori, A.M. and Onjoro, P.A. (2020) Abattoir Waste Use in Livestock Diets: Uganda’s Current Situation. International Journal of Research Innovations and Technology, 10, 129-134. https://doi.org/10.3329/ijarit.v10i1.48105</mixed-citation></ref><ref id="scirp.129165-ref27"><label>27</label><mixed-citation publication-type="other" xlink:type="simple">Ogello, E.O., Mlingi, F.T., Nyonje, B.M., Charo-Karisa, H. and Munguti, H.J. (2013) Can Integrated Livestock-Fish Culture Be a Solution to East Africa’s Food Insecurity? A Review. African Journal of Food, Agriculture, Nutrition and Development, 13, 8058-8075. https://doi.org/10.18697/ajfand.59.12920</mixed-citation></ref></ref-list></back></article>