Feed Additives Increase Intake Of

Feed Additives Increase Intake Of

<p> 1 Feed additives increase intake of tannin- and 2 terpene-rich plants in shrubland ecosystems 3 4 5 Jozo Rogosic1*, Zora Pilic2, Slaven Prodanovic3 and Savo Vuckovic3 6 8 1 University of Zadar, Department of Ecology, Agronomy and Aquaculture, Mihovila 9 Pavlinovića bb, 23000 Zadar, Croatia 10 11 2Department of Biology and Chemistry, Faculty of Natural Science, University of Mostar, 12 Ulica Matice hrvatske bb, 88000 Mostar, Bosnia/Herzegovina 13 14 3 University of Belgrade, Faculty of Agriculture, Nemanjina 6, 11080 Belgrade, Serbia 15 16 17 18 19 20 21 22 23</p><p>24</p><p>25</p><p>26</p><p>27</p><p>28</p><p>29</p><p>30</p><p>31</p><p>32</p><p>33 34*To whom correspondence should be addressed: e-mail: [email protected]</p><p>35Tel: 385 23 302 508</p><p>36Fax: 385 23 302 509</p><p>37 38 39 40 41Abstract - Maquis and garrigues are extensive shrubland vegetation types in the</p><p>42Mediterranean region that provide important habitat for wild and domestic herbivores.</p><p>43Although the majority of these shrubs are nutritious, virtually all contain secondary</p><p>44compounds that reduce their forage value. In six trials, we examined the effect of</p><p>45polyethylene glycol (PEG), activated charcoal (Ach) and number of shrubs offered on intake</p><p>46of Mediterranean shrubs by sheep and goats. We offered 3 shrubs in trial 1, 2 shrubs in trial 2</p><p>47and 1 shrub in trial. 3. Trials were conducted with 12 sheep and 12 goats (6 PEG vs. 6 control</p><p>48and 6 Ach vs. control). In trial 1, sheep receiving PEG ate more (P=0.002) total shrubs</p><p>49(Quercus ilex, Arbutus unedo and Pistacia lentiscus) than did controls, but no such treatment</p><p>50effect was found for goats. In trial 2, supplemental PEG had a positive effect (P<0.001) on</p><p>51total shrub intake for both sheep and goats when only 2 shrubs (Arbutus unedo and Pistacia</p><p>52lentiscus) of lower palatability were offered. In trial 3, supplemental PEG had a marked</p><p>53positive effect (P<0.001) on intake of Pistacia lentiscus in both sheep and goats. PEG</p><p>54supplemented goats ate more Pistacia lentiscus (39.6 g/kg) than did PEG supplemented sheep</p><p>55(28.1 g/kg), whereas control sheep and goats ate similar amounts (12.2 and 15.3 g/kg,</p><p>56respectively). In trial 4, we initially offered 3 shrubs (Juniperus phoenicea, Helichrysum</p><p>57italicum and Juniperus oxicedrus), then 2 shrubs (Juniperus phoenicea and Helichrysum</p><p>58italicum) in trial 5, and finally 1 shrub (Juniperus phoenicea) in trial 6. Goats ate more total</p><p>59shrub biomass than did sheep (45.7 ± 1.0 g/kg BW vs. 27.2 ± 0.7 g/kg BW, respectively) in</p><p>60trial 4, and there was no difference in shrub intake (P = 0.39) between Ach-treated animals</p><p>61and controls (mean 37.5 ± 0.8 g/kg BW). Supplemental Ach had a positive effect on total</p><p>62shrub intake for both sheep and goats in all 3 trials (trial 4, P < 0.001; trial 5, P < 0.001 and</p><p>63trial 6, P < 0.03), and goats ate more shrubs than did sheep in all 3 trials (P < 0.01).</p><p>64Regardless of experiment, both species of animals showed a numerical decrease in total shrub 65intake, with or without supplemental PEG/Ach, as the number of shrub species on offer</p><p>66decreased. Our findings support the hypothesis that plant biochemical diversity plays an</p><p>67important role in diet selection, thus enabling animals to better meet their nutritional needs</p><p>68and avoid toxicity. In addition, as the number of shrubs in the diet decreased (diminution of</p><p>69biodiversity), the concentration of terpenes and tannins in diet probably increased, so</p><p>70PEG/Ach had a greater impact on shrub intake. Finally, both PEG and Ach had the same</p><p>71influence on sheep and goats throughout the experiments, even though goats always ate more</p><p>72shrubs than did sheep. </p><p>73</p><p>74Key words: Feed additives, Activated charcoal, Polyethylene glycol, Biodiversity, Goats,</p><p>75Sheep, Mediterranean shrubs, Secondary compounds. </p><p>76</p><p>77 INTRODUCTION</p><p>78Mediterranean shrubby vegetation called “maquis” and “garrigue” are widespread throughout</p><p>79the Mediterranean Basin, including the Adriatic littoral of Croatia. In Croatia and elsewhere,</p><p>80these shrublands represent traditional grazing areas and are a significant source of forage for</p><p>81sheep and goats, particularly during the dry summer. </p><p>82 Secondary compounds (e.g., phenolics, terpenes, saponins, alkaloids, glycosides,</p><p>83tannins, etc.) often limit utilization of Mediterranean shrubs and adversely affect forage</p><p>84intake. Approximately 80% of the Mediterranean shrubby species contain tannins (Rhoades,</p><p>851979), often at levels of 10% or more in the dry matter (Levin, 1976). Phenolic compounds</p><p>86(total phenols, catechins, phenolic monomers, tannins, etc.) reduce digestibility and forage</p><p>87intake of animals grazing in the Myrto-Quercetum ilicis plant community, which is a major</p><p>88vegetation type of the Mediterranean maquis (Rogosic et al., 2007). Phenolic compounds also</p><p>89limit palatability, digestibility and intake of dominant forage shrubs such as rosemary 90garrigue Erico-Rosmarinetum officinalis (Rogosic and Ivankovic, 2004).</p><p>91 Terpenoids are the largest group of plant secondary chemicals, with over 30,000</p><p>92terpenes identified structurally (Little and Croteau, 1999).Terpenes have been found to</p><p>93decrease in vitro digestibility in ruminants, suggesting antimicrobial activity, especially if the</p><p>94rumen microbial population is not adapted to the compounds (Schwartz et al., 1980). Ngugi et</p><p>95al. (1995) reported sagebrush essential oil decreased bacterial numbers in deer rumen fluid,</p><p>96but observed no evidence of microbial adaptation. Actual effects of terpenes in vivo have</p><p>97been suggested to be less because of loss during mastication and rumination (Cluff et al.,</p><p>981982), eructation of warm volatiles (Pederson and Welch, 1982), and/or absorption from the</p><p>99rumen (Freeland and Janzen, 1974). Newbold et al. (2004) reported that an essential oil</p><p>100mixture fed to sheep caused no major effects on fermentation, rumen ammonia, protozoa</p><p>101numbers, or digestion, although they did observe reduced in sacco protein degradation.</p><p>102 A number of compounds have been examined for their potential to ameliorate adverse</p><p>103effects of tannins or terpenes, including polyethylene glycol (PEG) and activated charcoal</p><p>104(Ach). PEG has a high binding affinity for tannins and been shown to increase intake of</p><p>105tannin-rich forage (Pritchard et al., 1988, Silanikove et al., 1994), probably because increased</p><p>106binding of tannins alleviates adverse postingestive consequences such as lesions in the gut</p><p>107mucosa (Reed, 1995). Activated charcoal fed to lambs also increased intake of big sagebrush</p><p>108(terpene-rich) by 30% (Banner et al., 2000). </p><p>109 The objective of the study was to determine if supplemental PEG/Ach affected intake</p><p>110of 3 tannin- and 3 terpene-rich shrubs of the Myrto-Quercetum ilicis, maquis plant community</p><p>111by sheep and goats. We also determined if the effect of supplemental PEG/Ach was</p><p>112consistent when animals were offered different combinations of shrubs or single, less</p><p>113palatable shrubs Pistacia lentiscus and Juniperus phoenicea. We hypothesized that intake of</p><p>114shrubs by both sheep and goats would increase with supplemental PEG/Ach as the number of 115shrubs increased.</p><p>116 METHODS AND MATERIALS</p><p>117Study shrubs and animals</p><p>118The experiments were conducted at an experiment station 25 km from Split in the central part</p><p>119of the Croatian Adriatic coast (lat 43052` N; long 16023` E). Three tannin- and three terpene-</p><p>120rich shrubs of the Myrto-Quercetum ilicis, maquis plant community were examined in six</p><p>121experiments, each 10 day long. The first three PEG-trials included Quercus ilex L.</p><p>122(Fagaceae), Arbutus unedo L. (Ericaceae), and Pistacia lentiscus L. (Anacardiaceae), while in</p><p>123the second three Ach-trials include shrubs include Juniperus phoenicea L. (Cupressaceae),</p><p>124Helichrysum italicum (Roth) Guss. (Asteraceae), and Juniperus oxycedrus L. (Cupressaceae).</p><p>125All 6 experiments were conducted with sheep and goats and ran consecutively.</p><p>126 The experimental sheep (n = 12, mean weight 23.08 ± 1.59 kg) were a local breed that</p><p>127is a cross between the Croatian breeds “Pramenka” and “Wunterberg”. The experimental</p><p>128goats (n = 12, mean weight 19.83 ± 1.89 kg) were a mixture of domestic goats crossed with</p><p>129Saanen and Alpine breeds. Both species of animals had an approximately equal mix of both</p><p>130sexes. All experimental animals were raised on the same farm on the island of Brac (Central</p><p>131Dalmatia) utilizing the shrubby vegetation of the Mediterranean maquis. </p><p>132 All shrubs offered to sheep and goats were hand-harvested each week in the same</p><p>133location. Leaves and one-year old twigs, 10 cm long, were clipped and placed in bags. Within</p><p>134an hour the plant material was ground to 1 cm length with a chipper, mixed for uniformity,</p><p>135placed in woven, polyethylene feed sacks, and refrigerated at 4oC. Every morning before the</p><p>136trial, bags of shrubs to be fed that day were removed from cold storage and offered</p><p>137immediately to animals. </p><p>138</p><p>139Experimental protocol 140Animals housed individually (1.5 x 2 m pens) in covered stalls with wire mesh sides, and</p><p>141fresh water and trace mineral salt were provided free-choice. Prior to the experiments,</p><p>142baseline intake of alfalfa pellets was determined for each animal on days 1 to 5. After</p><p>143baseline was established, all sheep and goats (n = 12) were offered all six shrubs</p><p>144simultaneously from 0900 to 1300 hr for 5 days. Shrub intake was monitored, and 12 sheep</p><p>145and 12 goats were divided into two experimental groups in each experiment (n = 6) based on</p><p>146total shrub intake. Treatment groups were unaltered during the experiments and the same 12</p><p>147sheep and 12 goats were used in all 6 experiments, but between each experiment with shrubs</p><p>148baseline was re-established using alfalfa pellets and barley at a maintenance level for 3 days. </p><p>149Experiments 1; Trials 1 – 3. The objective of the first three experiments was to assess the</p><p>150effect of PEG and energy on intake of three tannin-rich shrubs. In the first experiment, three</p><p>151shrubs (Quercus ilex, Arbutus unedo and Pistacia lentiscus), in the second experiment two</p><p>152shrubs (Arbutus unedo and Pistacia lentiscus), while in the third experiment one shrub</p><p>153Pistacia lentiscus were offered to sheep and goats. At 0800 hours each morning on days 1 to</p><p>15410 treatment sheep and goats received 200 g ground barley mixed with 25 g of PEG, whereas</p><p>155control animals did not receive ground barley or PEG. Then, all animals were offered 200 g</p><p>156of each shrub simultaneously in separate food boxes from 0900 to 1400 hours daily for 10</p><p>157days. Animals and food boxes were checked every 30 min and additional ground material was</p><p>158added as needed. Food refusals were collected and shrub consumption was calculated. At</p><p>1591500 hours animals were offered varying amounts of alfalfa pellets calculated to provide 50%</p><p>160of their maintenance energy requirements (including barley; INRA, 1989). During the</p><p>161experiment 2 and 3, we repeated the same procedure. </p><p>162Experiments 2; Trials 4 – 6. The objective of these experiments was to determine the effect</p><p>163of activated charcoal and energy on intake of three terpene-rich shrubs. In the first</p><p>164experiment, three shrubs (Juniperus phoenicea, Helichrysum italicum and Juniperus 165oxycedrus), in the second experiment two shrubs (Juniperus phoeniceae and Helichrysum</p><p>166italicum), while in the third experiment one shrub Juniperus phoenicea were offered to sheep</p><p>167and goats. During the 10-day experiment, treatment animals were given a 200 g mixed</p><p>168preload of ground barley with 20 g Ach at 0800, while control animals did not receive ground</p><p>169barley or Ach. All animals were then fed 200 g of each shrub from 0900 to 1400 hours.</p><p>170Additional shrub material was added as necessary every 30 min until 1400. Each day refused</p><p>171shrubs were collected and biomass consumption was calculated. Likewise, as in the</p><p>172experiments 1-3, at 1500 hours animals were offered varying amounts of alfalfa pellets</p><p>173calculated to provide 50% of their maintenance energy requirements (including barley; INRA,</p><p>1741989). During the experiment 2 and 3 we, repeated the same procedure. </p><p>175Statistical analysis</p><p>176The total daily consumption of all shrubs offered in each experiment was used as the</p><p>177dependent variable in the analysis. The experimental design was a completely random design.</p><p>178Animals were a random factor in the mixed model analysis (SAS 2000). The model included</p><p>179treatment (PEG/Ach vs. control), species of animal (goats vs. sheep), and the species x</p><p>180treatment interaction; individual animals were nested within treatment and species. The</p><p>181model also used days as a repeated measure with all other interactions included. All analyses</p><p>182on shrub intake were adjusted for body weight (g/kg BW).</p><p>183</p><p>184 RESULTS</p><p>185Experiment 1. The effect PEG on forage intake of the Mediterranean shrubs</p><p>186Trial 1. Three shrubs offered to sheep and goats</p><p>187Goats and sheep differed in total shrub consumption. Regardless of treatment, goats ate</p><p>188substantially more total shrub biomass than did sheep (60.7 vs. 45.9 ± 2.6 g/kg BW, 189respectively). There was a trend (P=0.08) towards a positive PEG effect on total shrub intake,</p><p>190with PEG-supplemented animals consuming more total shrubs than controls (56.7 vs. 50.0 ±</p><p>1912.6 g/kg BW). </p><p>192 In general, when 3 shrubs were offered to sheep and goats, either with or without</p><p>193supplemental PEG, both treatment groups and both species of animals showed a tendency for</p><p>194increasing intake from the first to the last day in all experiments. Sheep receiving PEG ate</p><p>195more (P=0.002) total shrubs than did controls (Figure 1), but no such treatment effect was</p><p>196found for goats (Figure 2). Regardless of treatment, sheep and goats ate almost the same</p><p>197amount of total shrubs (34.4 g/kg BW for sheep vs. 41.4 g/kg BW for goats). Sheep and goats</p><p>198preferred Quercus ilex (18.58 g/kg BW) and Arbutus unedo (15.95 g/kg BW) over Pistacia</p><p>199lentiscus (3.34 g/kg BW).</p><p>200Trial 2. Two shrubs offered to sheep and goats</p><p>201Supplemental PEG positively affected (P<0.001) total shrub intake when only 2 shrubs</p><p>202(Arbutus unedo and Pistacia lentiscus) of lower palatability were offered (Figure 1 and 2).</p><p>203Both sheep and goats fed supplemental PEG ate numerically more Pistacia lentiscus (17.54</p><p>204g/kg BW) compared to non-supplemented sheep or goats (7.57 g/kg BW) and especially</p><p>205compared Pistacia lentiscus in experiment 1 (3.34 g/kg BW). </p><p>206Trial 3. One shrub - Pistacia lentiscus offered to sheep and goats</p><p>207Supplemental PEG had a marked positive effect (P<0.001) on intake of Pistacia lentiscus in</p><p>208both sheep and goats (Figure 1 and 2). PEG-supplemented goats ate more Pistacia lentiscus</p><p>209(39.6 g/kg BW) than did PEG supplemented sheep (28.1 g/kg BW), whereas control sheep</p><p>210and goats ate similar amounts (12.2 and 15.3 g/kg BW, respectively). </p><p>211Experiment 2. The effect Ach on forage intake of the Mediterranean shrubs</p><p>212Trial 4. Six shrubs offered to sheep and goats 213As in experiment 1, goats again ate more shrubs than did sheep throughout experiment 4</p><p>214(P<0.01, Figure 3 and 4). Ach-treated sheep and goats ate more total shrubs than did control</p><p>215animals (P=0.002; 37.9 ± 1.4 g/kg BW versus 28.2 ± 1.3 g/kg BW). There were no species x</p><p>216treatment or treatment x day interactions (P > 0.50), but there was a species x day interaction</p><p>217as both goats and sheep increased intake of the 3 shrubs over the period (P=0.004; Figure 3</p><p>218and 4). Even though sheep and goats differed in total amounts of shrubs eaten, the rank order</p><p>219of the amount eaten for each shrub species was essentially the same for both sheep and goats.</p><p>220The mean amounts eaten of the shrubs across all treatments and animal species were:</p><p>221Juniperus oxycedrus (20.35 g/kg BW), Helichrysum italicum (18.16 g/kg BW) and Juniperus</p><p>222phoenicea (15.75 g/kg BW).</p><p>223Trial 5. Two shrubs offered to sheep and goats</p><p>224Goats had a higher total intake when offered 2 shrubs than did sheep (P=0.0003; 34.5 ± 0.9</p><p>225g/kg BW versus 24.3 ± 0.9 g/kg BW; Figure 3 and 4). Sheep and goats fed Ach ate more</p><p>226shrubs than did control animals (P=0.001; 33.9 ± 0.8 g/kg BW versus 24.8 ± 1.1 g/kg BW).</p><p>227There were no species x treatment or species x day interactions (P > 0.50), but there was a</p><p>228treatment x day interaction (P = 0.03) as charcoal-treated animals increased intake of the 2</p><p>229shrubs over the 5-day period more than the control animals (Figure 3). </p><p>230Trial 6. One shrub – Juniperus phoenicea offered to sheep and goats</p><p>231There was a treatment x day (P = 0.03) interaction as Ach-treated animals, particularly sheep,</p><p>232increased intake of Juniperus phoenicea over time compared to control animals (Figure 3 and</p><p>2334). There was also a species x day interaction (P = 0.02) as sheep increased intake over the</p><p>234period more than did goats even though sheep ate less Juniperus phoenicea biomass</p><p>235compared to goats. 236 DISCUSSION</p><p>2371. Effect of PEG on Mediterranean tannin rich shrubs intake</p><p>238PEG is a polymer that binds to tannins irreversibly over a wide range of pH, thus alleviating</p><p>239the negative effects of tannins (Landau et al., 2000). Supplemental PEG increases intake of</p><p>240tannin-containing plants by sheep and goats (Pritchard et al., 1992; Titus et al., 2000, 2001)</p><p>241and cattle (Hanningan and McNeil, 1998). Nevertheless, it is very interesting that when sheep</p><p>242and goats were offered 6 shrubs (Rogosic et al., 2007a), and when goats were offered 3</p><p>243shrubs, PEG had no beneficial effect on intake (Figure 2). In general, as the number of shrubs</p><p>244in the diet decreased, the impact of PEG on intake of shrubs increased. PEG alone increased</p><p>245consumption of the 3-shrub mix by sheep. When 3 species were offered to sheep (trial 1), and</p><p>246when 2 or 1 species offered to goats (trials 2 and 3), PEG and energy substantially increased</p><p>247intake of shrubs high in tannin. </p><p>248 Interactions among nutrients, toxins and PEG affected use of shrubs. For example, in</p><p>249trial 2 the relatively unpalatable shrub Pistacia lentiscus was not avoided when offered with</p><p>250another more palatable shrub (Arbutus unedo) even though animals were not forced to eat</p><p>251Pistacia lentiscus. Further, goats and sheep receiving PEG and energy in the 2-shrub trial ate</p><p>252much more of both shrubs than did control animals, indicating the effectiveness of</p><p>253PEG/barley in reducing the impacts of tannins from Pistacia lentiscus and Arbutus unedo</p><p>254(Villalba et al., 2002a). </p><p>255 Food selection by herbivores depends on nutritional state (Villalba et al., 2002a). In</p><p>256trials 2 and 3, the control animals did not receive supplemental feed. When ingesting toxins</p><p>257entails a metabolic cost, herbivores are likely to respond by modifying their feeding behavior</p><p>258(Foley et al., 1999). Supplemental macronutrients increase intake of foods that contain toxins</p><p>259as diverse as lithium chloride (Wang and Provenza, 1996), terpens and tannins (Rogosic et al.,</p><p>2602007), menthol (Illus and Jessop, 1996), and quebracho tannin (Villalba et al., 2002a). 261Consequently, the ability of herbivores to consume shrubs high in secondary compounds will</p><p>262depend on the interaction between the quantity and quality of nutrients available and the</p><p>263classes of toxins present in the mix of plant species (Provenza et al. 2003). </p><p>2642. Effect of Activated Charcoal on Mediterranean Terpenes Rich Shrubs Intake</p><p>265Activated charcoal adsorbs phytochemicals in shrubs and facilitates their excretion via the</p><p>266feces (Buck and Bratich, 1986). Positively charged surfaces in activated charcoal bind with</p><p>267the negatively charged molecular surface of most toxins, decreasing their bioaviability (Poage</p><p>268et al., 2000). In trial 4, when 3 shrubs were offered, sheep and goats supplemented with 200 g</p><p>269barley + 20 g Ach (treatment groups) ate more shrubs than sheep and goats (control group),</p><p>270which is not supplemented with Ach nor energy. This is similar to other results when lambs</p><p>271were supplemented with charcoal-barley mix (P = 0.71, 1.7 g charcoal/kg 0.75) and they ate</p><p>272more sagebrush than lambs supplemented only with barley (Banner et al., 2000). </p><p>273 When 3 shrubs were offered to sheep and goats, and controls were given energy as</p><p>274well, there was a positive effect from Ach on intake of 3 shrubs high in terpenes (Juniperus</p><p>275phoenicea, Helichrysum italicum and Juniperus oxicedrus; trial 4). When 2 shrubs (Juniperus</p><p>276phoenicea and Helichrysum italicum; trial 5) or 1 shrub (Juniperus phoenicea trial 6) was</p><p>277offered to sheep and goats, Ach and energy together substantially increased intake of shrubs</p><p>278high in terpenes (Figures 3 and 4). Previous work has shown that lambs that learned to eat</p><p>279foods containing a variety of toxins ate more when they could select 2 of the foods rather than</p><p>280only 1 (Villalba et al., 2004). </p><p>281 Further, goats and sheep receiving charcoal and energy in trials 4 – 6, when offered 3</p><p>282 2  1 shrub ate much more shrub than did controls, indicating the effectiveness of charcoal</p><p>283and barley in reducing the impacts of terpenes from Juniperus phoenicea, Helichrysum</p><p>284italicum and Juniperus oxicedrus. Other studies with sagebrush (Artemisia sp.) in the U.S.</p><p>285also have shown that supplemental energy impacted shrub intake when given in combination 286with activated charcoal (Banner et al., 2000; Villalba et al., 2002b). </p><p>2873. Influence of biological/biochemical diversity on shrub selection</p><p>288The vast majority of Mediterranean shrubs contain secondary compounds, thus browsing</p><p>289sheep and goats can not avoid ingesting various phytotoxins that commonly occur in those</p><p>290plants (Rogosic, et al., 2007). Most secondary compounds are ingested in amounts too low to</p><p>291cause acute symptoms of poisoning and death, and we saw no overt adverse signs of toxicity.</p><p>292This study confirmed the common view that mixed diets improve food intake (Freeland and</p><p>293Choquenot, 1990). The kinds and different amount of nutrients and toxins in the</p><p>294Mediterranean shrubs fed to sheep and goats probably influenced toxin satiation, which is not</p><p>295fixed but dynamically determined by the physiological state of animal relative to the quality</p><p>296and quantity of nutrients and toxins available (Villalba et al., 2002a). In essence, toxins cause</p><p>297herbivores to eat a variety of plants to meet their needs for nutrients because the pathways of</p><p>298detoxification are saturable (Foley et al., 1999). Thus, as animals satiate on particular toxins</p><p>299they must find alternative food sources containing complementary nutrients and toxins</p><p>300(Villalba al. al., 2002b). The satiety hypothesis and ensuing nutrient-nutrient, nutrient-toxin,</p><p>301and toxin-toxin interactions help to explain the dynamics of these interactions and the benefits</p><p>302of varied diets (Provenza et al., 2003).</p><p>303 As the number of shrubs decreased from trial 1 to trial 3 and from trial 4 to trial 6, the</p><p>304concentration of tannins and terpenes in shrub biomass offered to animals increase, so the</p><p>305total shrub intake decreased numerically for both sheep and goats. In other words, these</p><p>306results clearly showed that combinations of more shrubs offered to animals promoted greater</p><p>307intake. These results are consistent with the satiety hypothesis (Provenza et al., 2003) that</p><p>308interactions among flavors, nutrients, and toxins (i.e., secondary compounds) lead to</p><p>309enhanced intakes, even of lower preference shrub such as Juniperus phoenicea and Pistacia</p><p>310lentiscus. 311 Depending on prevailing conditions, sheep and goats browsing on Mediterranean</p><p>312shrubby vegetation may be able to mix their diets to provide sufficient energy and protein</p><p>313while reducing toxin loads. The shrubs offered in these experiments varied in amounts of</p><p>314macronutrients (Rogosic et al., 2006), and also in kinds and amounts of secondary compounds</p><p>315such as terpenes (high terpenes: Juniperus phoenicea, Helichrysum italicum and Juniperus</p><p>316oxycedrus), tannins (high tannins: Arbutus unedo, Quercus ilex and Pistacia lentiscus). </p><p>317 Our results suggest that interaction between macronutrients, PEG (in trial 1 - 3) and/or</p><p>318Ach (in trial 4 - 6), flavor and toxins influenced how sheep and goats mixed their diets and</p><p>319utilized shrubs, and that supplemental macronutrients enhanced intake of food that contain</p><p>320terpenes and tannins. Likewise, different concentrations of nutrients in plant species may have</p><p>321different effects on selection of food by sheep and goats depending on the classes and</p><p>322concentration of toxins in maquis plant community. </p><p>323</p><p>324 CONCLUSIONS</p><p>325Shrubby vegetation of the Mediterranean maquis dominates rangelands throughout the</p><p>326Mediterranean Basin, including the Adriatic littoral of Croatia. Sheep and goats are an</p><p>327environmentally and economically sound alternative for using the forage potential of</p><p>328Mediterranean shrubs. Increasing use of these shrubs by livestock would likely enhance the</p><p>329production of grasses and forbs and create a more diverse mix of plants. Grazing by livestock</p><p>330also reduces the likelihood and the impacts of fires, common in these regions. </p><p>331 Most Mediterranean shrubs contain large quantities of secondary compounds that limit</p><p>332intake and cause animals to eat a variety of foods. In this study, as the number of shrub</p><p>333species in the diet decrease (trials 1 - 3 and trails 4 - 6), so too did intake. Both PEG and Ach</p><p>334supplement positively influenced shrub intake when offered 3  2 1 shrubs to sheep and</p><p>335goats. Likewise PEG and Ach had the same influence on sheep and goats throughout the 336experiments, and it had the most influence on both sheep and goats when shrub availability</p><p>337was reduced. </p><p>338 Our findings suggest that biochemical diversity plays a very important role in</p><p>339herbivore’s diet selection, enabling animals to better meets their nutritional needs and avoid</p><p>340toxicity. </p><p>341</p><p>342 REFERENCES 343 344Banner, R. E., J. Rogosic, E. A. Burrit, and Provenza, F.D., 2000. Supplemental barley and </p><p>345 charcoal increase intake of sagebrush by lambs. J. Range Manage. 53:415-420.</p><p>346Buck W.B. and Bratic, P.M., 1986. Activated charcoal: Preventing unnecessary death by </p><p>347 poisoning. 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B., and Croteau, R.B., 1999. Biochemistry of essential oil terpenes. In: Teranishi </p><p>373 (Ed.), Flavor Chemistry: 30 Years of Progress. Kluwer Academic/Plenum Publ., New </p><p>374 York, NY. pp. 239-253.</p><p>375Newbold, C. J., McIntosh, F.M., Williams, P., Losa, R. and Wallace, R.J., 2004. Effects of a </p><p>376 specific blend of essential oil compounds on rumen fermentation. Anim. Feed Sci. </p><p>377 Tech. 114:105-112.</p><p>378Ngugi, R. K., Hinds, F.C. and Powell, J., 1995. Mountain big sagebrush browse decreases dry</p><p>379 matter intake, digestibility, and nutritive quality of sheep diets. J. Range Manage. </p><p>380 48:487-492.</p><p>381Pederson, J. C., and Welch, B.L., 1982. Effects of monoterpenoid exposure on ability of </p><p>382 rumen inocula to digest a set of forages. J. Range Manage. 35:500-502.</p><p>383Poage G.W., Scott, C.B., Bisson, M.G. and Hartman, F.S., 2000. Activated charcoal </p><p>384 attenuates bitterweed toxicosis in sheep. J. 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Sci. 80:2099-</p><p>431 2109.</p><p>432Villalba, J.J., Provenza, F.D. and Han, G., 2004. Experience influences diet mixing by </p><p>433 herbivores: implications for plant biochemical diversity. OIKOS 107: 100 –109.</p><p>434Welch, B.L. and McArthur, E.D., 1981. Variation of monoterpenoid content among </p><p>435 subspecies and accessions of Artemisia tridentata grown in a uniform garden. J. Range</p><p>436 Manage. 34: 380-384. 437Wang, J. and Provenza, F.D., 1996. Food deprivation affect preference of sheep for foods </p><p>438 varying in nutrients, and a toxin. J. Chem. Ecol. 23:275-288.</p><p>439 440 441 442 443 444 445 446 447 448 449 450 451 452 453 454 455 456 457 458 459 460 461</p><p>Sheep 50 3 shrubs 2 shrubs 1 shrub Trial 1 Trial 2 Trial 3 a 40 a</p><p>) Quercus ilex . b</p><p> w Arbutus unedo . 30 b a</p><p>Pistacia lentiscus g k / g (</p><p> b</p><p> e 20 k a t</p><p> n b I 10</p><p>0 p p p u p p p u u o u u u ro ro r o ro ro g g -g r g g - - L g - - L G - L G O E O G O E R P R E R P T T P T N N N O O O C C C 462 463Figure 1. Total shrub intake by sheep offered three (Quercus ilex, Arbutus unedo, and </p><p>464Pistacia lentiscus), two (Arbutus unedo, and Pistacia lentiscus), or one (Pistacia lentiscus) </p><p>465shrub species. Different letters indicate that charcoal-treated animals and controls differed </p><p>466(Trial. 1, P= 0.002; Trial 2, P 0.001; Trial 3, P 0,001) within an experiment.</p><p>467</p><p>Goats 60 3 shrubs 2 shrubs 1 shrub Trial 2 Trial 3 Trial 1 a 50 a )</p><p>. a a Quercus ilex w 40 .</p><p> b Arbutus unedo</p><p> g Pistacia lentiscus k / 30 g</p><p>( b</p><p> e k a</p><p> t 20</p><p> n b I</p><p>10</p><p>0 p u p p p p u u u u p ro o o o o u g r r r r o - g -g -g -g r G - L -g E L G G L P O E O E R P R P O T T R N N T O N O C O 468 C C</p><p>469</p><p>470Figure 2. Total shrub intake by goats offered three (Quercus ilex, Arbutus unedo, and Pistacia</p><p>471lentiscus), two (Arbutus unedo, and Pistacia lentiscus), or one (Pistacia lentiscus) shrub </p><p>472species. Different letters indicate that charcoal-treated animals and controls differed (Trial 1, </p><p>473P= 0.002; Trial 2, P 0.001; Trial 3, P 0.001) within an experiment.</p><p>474</p><p>475 482 481 480 479 478 477 476 experiment. experiment. controls(Trial1,P differed and animals ( one italicum, bysheep( intake offered 3.Totalshrub three Figure</p><p>S Intake (g/kg b.w.) h 15 20 25 30 35 10 Juniperus phoenicea e</p><p> e 0 5 p C and S h h a e r e c p o</p><p>Juniperus oxycedrus a C l o shrubs3 n 1 Trial tr a o l</p><p>S h ) shrub species. Different letters indicate that charcoal-treated charcoal-treated that indicate letters species. Different ) shrub e e</p><p> p b C S h h a r e c e</p><p>), two( o p a C l</p><p> o a</p><p> n shrubs2 tr Trial2  o</p><p>0.01; Trial 2, P= 0.001; Trial3,P=an Trial2,P= 0.02)within 0.001; 0.01; l Juniperus phoenicea Juniperus phoenicea</p><p>S h e b e p C</p><p>Juniperus phoenicea, Helichrysum Helichrysum Juniperus phoenicea, S h h a e r e c p o a C l a o n tr</p><p> o 1shrub l Trial3 and and Juniperusoxycedrus Helichrysumitalicum Juniperusphoenicea b Helichrysum italicumHelichrysum ), or 491 490 489 488 487 486 485 484 483 experiment. experiment. controls(Trial1,P differed and animals ( one italicum, bygoats( intake offered 4.Totalshrub three Figure Intake (g/kg b.w.) Juniperus phoenicea 10 20 30 40 50 0</p><p> and G o a t </p><p>Juniperus oxycedrus C h a r c Trial 1</p><p> o a a G l o a t </p><p>C 3 shrubs</p><p>) shrub species. Different letters indicate that charcoal-treated charcoal-treated that indicate letters species. Different ) shrub o n tr G o b o l a t C h ), two( a r c o a l a</p><p> G 2shrubs 0.01; Trial 2, P= 0.001; Trial3,P=an Trial2,P= 0.02)within 0.001; 0.01; Juniperus phoenicea Juniperus phoenicea o Trial2 a t C o n tr G o l b o a Juniperus phoenicea, Helichrysum Helichrysum Juniperus phoenicea, t C h a r c o a l a G o</p><p> and and a 1shrub </p><p> t Trial3 C o</p><p>Helichrysum italicumHelichrysum n tr o b</p><p> l Juniperus oxycedrus Helichrysumitalicum Juniperus phoenicea ), or</p>

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