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	<title>exotics Archives - TheRanch at Camp Ka Hui Ana</title>
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	<description>Exclusive Trophy Whitetail Deer Hunting in Southwest Texas</description>
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	<title>exotics Archives - TheRanch at Camp Ka Hui Ana</title>
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		<title>Spike Culling: Effective Deer Management or Myth? &#124; The Ranch</title>
		<link>https://theranchtx.us/spikes-to-cull-or-not-to-cull/?utm_source=rss&#038;utm_medium=rss&#038;utm_campaign=spikes-to-cull-or-not-to-cull</link>
		
		<dc:creator><![CDATA[Chase Nunez MS PhD]]></dc:creator>
		<pubDate>Sat, 19 Oct 2024 20:54:04 +0000</pubDate>
				<category><![CDATA[Deer Herd]]></category>
		<category><![CDATA[Wildlife Management]]></category>
		<category><![CDATA[deerhunting]]></category>
		<category><![CDATA[exotics]]></category>
		<category><![CDATA[hunting]]></category>
		<category><![CDATA[predator control]]></category>
		<category><![CDATA[predators]]></category>
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		<category><![CDATA[texas deer hunting]]></category>
		<category><![CDATA[texas hunting]]></category>
		<category><![CDATA[Trophy Whitetail Deer Hunting]]></category>
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					<description><![CDATA[<p>Debating whether to cull spikes from your herd? Our latest article explores the science and misconceptions behind spike culling. Discover what’s best for your wildlife management.</p>
<p>The post <a href="https://theranchtx.us/spikes-to-cull-or-not-to-cull/">Spike Culling: Effective Deer Management or Myth? | The Ranch</a> appeared first on <a href="https://theranchtx.us">TheRanch at Camp Ka Hui Ana</a>.</p>
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									<p>Will harvesting “spike” white-tailed deer help grow <a href="https://theranchtx.us/product/trophy-whitetail-deer-hunting-package/">bigger bucks?</a> The foundation of many wildlife management plans are often built on one side of the other of the argument with solid reasoning either way. This age-old question among white-tailed deer hunters, ranchers, and managers, is actually a question of two parts– 1. are spike white-tailed bucks genetically inferior and, if so, 2. will culling spike bucks improve the antler size among the white-tailed deer herd. To thoroughly but briefly deconstruct the sides, we must clearly define some terminology, clarify some misnomers on the topic, and breakdown when and how the reasons ‘to cull or not to cull’ situationally apply.</p><p>Using the Texas Parks &amp; Wildlife Department definition, a spike in the case of this writing is a white-tailed deer buck with at least one unbranched antler.<sup>1</sup> Our definition of an unbranched antler is a single beam or tine and does not include “cactus”, perruque, or broken antlers. We are excluding these from our criteria because cactus or perruque antlered bucks are often associated with testicular and/or testosterone related issues and broken antlers are often environmentally related (fighting, hit by a car, etc.). Deer with antlers that have not broke through the skin of the scalp are often called “nubbin” or “button” bucks are considered antlerless, not spike bucks. Culling is the act of selectively removing an animal from the population as a means of controlling or removing undesirable characteristics (bad genetics, diseases, etc.). And lastly, just so we’re clear, bigger bucks is not indicative of body size or mass… Although good body condition can be an indication of good health, our definition of bigger bucks is white tailed deer with larger, better scoring bone (antlers) on their heads.</p><h4>Myths</h4><p>Now to dispel a couple of myths. One common misconception about white-tailed deer spikes is this idea that “once a spike, always a spike”. This is simply not true; not that a spike couldn’t be a spike it’s whole life, but most in fact are only a spike for their first set of antlers and progressively get larger, better scoring antlers each year with age and nutrition.<sup>2</sup> A study in south Texas conducted by Stephen F. Austin State University researchers found that the average spike with 3 legal points or less at 1.5 years old will be at or above the herd average number of points and Boone and Crocket score by 3.5–5.5 years old.<sup>2</sup> Another major misconception is that all (or most) spikes are caused by poor antler genetics. The genetic aspect certainly plays a role, but in actuality, there are numerous reasons that can cause spike antlers among white-tailed deer at any stage of life. This may include injuries or infections at the antler pedicle (the base of the skull where antlers regenerate from each antler growing season) from fighting, motor vehicle collisions, or casting previous year’s antlers, opposite hind limb injuries, nutritional deficiencies, antler breakage, testicular injuries or infections, testosterone issues, harsh weather conditions during buck fawn gestation, or simply age.<sup>1,3,4</sup> In fact, a large portion of single spike-antlered bucks (one antler has branches and one is a spike) are caused by good ol’ nature and nurture (environmental and/or health) rather than genetics.</p><p>One study conducted in Alabama found that 62% of single spike-antlered bucks were caused by external factors like those described above.<sup>3</sup> Furthermore, 92% of <a href="https://theranchtx.us/trophy-deer-hunting/">white-tailed bucks</a> with two spike antlers are a yearling (about 1.5 years old) with their first set of antlers.<sup>1</sup> But, just because most double-sided spike bucks are yearlings does not mean most yearlings are spikes; only about 25%–33% of yearlings are spikes.<sup>1</sup></p>								</div>
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									<h4>Does that mean that spikes are genetically inferior?</h4><p>An argument can be made that there is a genetic aspect in both the size of antlers and susceptibility to injury, infection, or disease that may otherwise cause spike antlers. But the same argument can be made that a gene that is associated with large antlers could also be associated with more breakable antlers, or some other double-edged genetic sword. Under the assumption that the genetic influence on external reasons for spike antlers is obsolete by canceling itself out, the size of antlers are based on antler genetics, nutrition, and age. When available forage and nutrition are sparse, the percentage of yearling spikes will increase. But, if observing three visibly healthy same-aged bucks on a ranch that are likely to have received similar nutrition, and one of the three bucks is a spike while the other two are 6-point or 8-point bucks, the spike buck likely has comparatively inferior antler genetics.</p><p>Does that mean culling spikes will improve the antler quality among the deer herd? The short answer, it depends. There is evidence that culling will not influence antler size of the average low fenced ranch white-tailed deer herd, regardless of culling criteria.<sup>2,5</sup> The reasoning boils down to too little control; over the deer movement, over neighbors culling criteria (or lack thereof), the genes present in the herd, etc. But there is much more control over management goals and strategies when discussing deer herd management of a closed herd like that behind a game-proof fence or in a geographic area with limited migration (islands, steep surrounding mountains, etc.). In these more controllable situations, the use of selective culling to improve antler characteristics is more likely to prove effective.<sup>5</sup></p><p>Ultimately, my philosophy is, if the buck white-tailed deer population is high and numbers need to be thinned, you can’t go wrong shooting spikes, especially from age classes older than 1.5 years. If the buck white-tailed deer population is low, let the spikes go and grow, because there is plenty of evidence that a spike can explode into a respectable buck with age and good nutrition.<sup>2</sup></p><h4><strong>Bibliography:</strong></h4><ol><li>Texas Parks and Wildlife Department. 2006. <a href="https://tpwd.texas.gov/landwater/land/wildlife_management/deer/antler_restrictions">Antler Restrictions.</a> Accessed September 1, 2024.</li><li>Koerth BH, Kroll JC. 2008. Juvenile-to-adult antler development in white-tailed deer in south Texas. <em>Journal of Wildlife Management </em>72(5):1109–1113.</li><li>Karns GR, Ditchkoff SS. 2013. Trauma-induced malformed antler development in male white-tailed deer. <em>Wildlife Society Bulletin</em> 37(4):832–837.</li><li>Mississippi State University Deer Ecology and Management Lab. 2019. Antler Abnormalities. . Accessed September 1, 2024.</li><li>Webb SL, Demarais S, Strickland BK, DeYoung RW, Kinghorn BP, Gee KL. 2012. <a href="https://www.msudeer.msstate.edu/abnormalities.php#:~:text=Damage%20to%20the%20antler%20during%20the%20velvet%20stage%20can%20result,opposite%20side%20antler%20grows%20abnormally">Effects of selective harvest on antler size in white-tailed deer: a modeling approach.</a> <em>Journal of Wildlife Management</em> 76(1):48–56.</li></ol>								</div>
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		<p>The post <a href="https://theranchtx.us/spikes-to-cull-or-not-to-cull/">Spike Culling: Effective Deer Management or Myth? | The Ranch</a> appeared first on <a href="https://theranchtx.us">TheRanch at Camp Ka Hui Ana</a>.</p>
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		<title>Assessing Various Predator Crossing Deterrents for Fence Line Management on A White-Tailed Deer Ranch in Southern Texas</title>
		<link>https://theranchtx.us/assessing-various-predator-crossing-deterrents-for-fence-line-management-on-a-white-tailed-deer-ranch-in-southern-texas/?utm_source=rss&#038;utm_medium=rss&#038;utm_campaign=assessing-various-predator-crossing-deterrents-for-fence-line-management-on-a-white-tailed-deer-ranch-in-southern-texas</link>
		
		<dc:creator><![CDATA[Chase Nunez MS PhD]]></dc:creator>
		<pubDate>Sat, 21 Sep 2024 19:15:09 +0000</pubDate>
				<category><![CDATA[Predator Control]]></category>
		<category><![CDATA[Wildlife Management]]></category>
		<category><![CDATA[deerhunting]]></category>
		<category><![CDATA[exotics]]></category>
		<category><![CDATA[hunting]]></category>
		<category><![CDATA[predator control]]></category>
		<category><![CDATA[predators]]></category>
		<category><![CDATA[success rate]]></category>
		<category><![CDATA[texas deer hunting]]></category>
		<category><![CDATA[texas hunting]]></category>
		<category><![CDATA[Trophy Whitetail Deer Hunting]]></category>
		<guid isPermaLink="false">https://theranchtx.us/?p=6618</guid>

					<description><![CDATA[<p>Explore effective predator crossing deterrents for fence-line management on a Southern Texas white-tailed deer ranch. Learn how these strategies can improve fawn survival and hunting opportunities at The Ranch.</p>
<p>The post <a href="https://theranchtx.us/assessing-various-predator-crossing-deterrents-for-fence-line-management-on-a-white-tailed-deer-ranch-in-southern-texas/">Assessing Various Predator Crossing Deterrents for Fence Line Management on A White-Tailed Deer Ranch in Southern Texas</a> appeared first on <a href="https://theranchtx.us">TheRanch at Camp Ka Hui Ana</a>.</p>
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									<p class="p1">In south Texas, predation of white-tailed deer (<i>Odocoileus virginianus</i>) fawns and nesting game birds like wild turkeys (<i>Maleagris gallopavo</i>) and bobwhite quail (<i>Colinus virginianus</i>) is a common threat during the late winter, spring, and early summer months. During this time of year, new mothers and young are most vulnerable<span class="s1"><sup>6</sup></span>– a fact of life that predators rely on as a primary source of nutrition for their own young survival. Fawn and nest predation includes both mammalian and avian culprits, but avian predators are more difficult to manage from a regulatory aspect. Mammalian predators of frequent concern include, but are not limited to, coyotes (<i>Canis latrans</i>), raccoons (<i>Procyon lotor</i>), bobcats (<i>Lynx rufus</i>), grey foxes (<i>Urocyon cinereoargenteus</i>), hog-nosed skunks (<i>Conepatus leuconotus</i>), opossums (<i>Didelphis virginiana</i>), badgers (<i>Taxidea taxus</i>), feral hogs (<i>Sus scrofa</i>), nine-banded armadillos (<i>Dasypus novemcinctus</i>), feral cats (<i>Felis catus</i>), and feral dogs (<i>Canis familiaris</i>)<span class="s1"><sup> 2,3,4,6</sup></span>. Although the effects of mammalian predator management on nesting success and survival is largely unknown, there has been evidence showing it results in significant improvements for fawn survival and recruitment<span class="s1"><sup>3</sup></span>.</p><p class="p1">There are many methods for controlling predator population sizes, but snare trapping on fence-lines is a time- and cost-effective method that is often utilized for trapping mammalian predators like coyotes in southern Texas<span class="s1"><sup>5</sup></span>. A snare is one of the oldest and most rudimentary traps, constructed from a simple wire or cable loop with a locking device that creates a cinch effect– as the animal pulls harder, the loop locks tighter and tighter around the animal’s body<span class="s1"><sup>1,5</sup></span>. Snares can, however, be set for more species-specific captures, if desired, with cable stops (allows smaller animals to escape and larger animals to avoid leg catches) and trap set design (loop size, cable-size, trap placement location, etc.)<span class="s1"><sup>1</sup></span>.</p>								</div>
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									<p class="p1"><span style="font-style: inherit; font-weight: inherit;">For snares to be most effective, it is recommended to trap on fence-lines constructed of net-wire</span><span class="s1" style="font-style: inherit; font-weight: inherit;"><sup>5</sup></span><span style="font-style: inherit; font-weight: inherit;">, which forces most predators underneath and creates a habitual travel route that is easily accessible and advantaged for trappers. Identifying fence-line travel paths with higher traffic allows property and/or wildlife managers to trap predators more efficiently and effectively. Filling in holes that traverse under net-wire fencing forces predators to re-dig or dig new holes under the fence; these new holes indicate recent and potentially frequently used areas and can be leveraged for snare trap sets. It is not known if different hole filling substrates (dirt, concrete, razor wire, cactus, thorny brush, etc.) are more effective than others at deterring predator re-digs, but reduced re-dig activity could concentrate the travel across fence-lines and increase the frequency of trapping success with less effort. This experiment sought to determine if different filler materials made a difference in fence-line hole re-dig activity.</span></p><p class="p1">The experiment was conducted over a 39-day period (2/2/2024–3/11/2024) on a 546-acre white-tailed deer ranch approximately 12 miles East from Dilley, Texas in La Salle County. The perimeter of the property is surrounded by an eight-foot-tall game-proof StaTite net-wire fence with two vehicle drive-through gates over cattle guards. There are no livestock on the ranch, but white-tailed deer are managed extensively for a hunting operation.</p><p class="p1">The ranch shape is an approximate rectangle with 3.8 miles of perimeter fencing. A total of 40 predator-made holes traversing the game proof fencing were identified and enrolled in the study; 16 holes on the southwestern fence (1.2 miles), two holes on the northwestern fence (0.7 miles), 15 holes on the northeastern fence (1.2 miles), and seven holes on the southeastern fence (0.7 miles). When a hole was discovered, notes were recorded about the hole to better estimate the primary culprit of the hole in question; these notes included measurement of the hole size (width and height), notes on the type and density of the surrounding vegetation, suspected culprits (based on tracks, scat, hair caught in the fence, etc.), and the estimated frequency of use based on trail wear. Holes were filled in with either dirt only (as a control), a mix of dirt and prickly-pear cactus (<i>Opuntia basilaris platypuntia</i>) paddles, or a mix of dirt and thorny brush clippings from honey mesquite (<i>Prosopis glandulosa</i>), blackbrush (<i>Coleogyne ramosissima</i>), and allthorne (<i>Koeberlinia spinosa</i>). The filler used for each hole was rotated so that the order was dirt–dirt/cactus–dirt/thorny brush–dirt–dirt/cactus–… so that holes were randomly filled and so there was an even number of samples distributed across the three test groups. Holes were checked after four-, 14-, and 23-days for re-dig activity. If a hole was re-dug, measurements and notes were recorded for the new hole and it was then re-filled with the next filler in the order from the previous filler (i.e. if the previous filling attempt was dirt only, the refill was with dirt/cactus). A successful re-dig was defined as a hole that traversed completely underneath the net-wire fence. Holes at the end of the experiment were used for future snare trap sites.</p>								</div>
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									<h5 class="p1"><b>Results and Discussions</b></h5><p class="p1"><b> </b>Predator holes under the fence had a size range of 7–32 inches wide (w) and 3.5–14 inches deep (h), with an average hole size of 15.9 inches (w) by 7.5 inches (h). The suspected culprits of holes, with occasional evidence on multiple suspects, included coyotes (n=34), javelina (<i>Pecari tajacu</i>; n=7), raccoons (n=5), armadillos (n=2), and bobcats (n=1). Re-dug holes (n=20) ranged in size from 4–22 inches (w) and 3–10 inches (h). The average size of a re-dug hole was 10.9 inches (w) by 6.4 inches (h). The suspected culprits of re-dig activity, with occasional evidence of multiple species at one re-dig site, were coyotes (n=15), bobcats (n=4), javelina (n=3), raccoons (n=2), and skunks (n=1). Vegetation type and the estimated frequency of use did not seem to predict re-dig activity. The hole size associated with each species determined by evidence is shown in Table 1. Although there is a high degree of overlap in hole dimensions between target species and non-target species (javelina), hole size and evidence used simultaneously can inform the trapper of the most likely species to travel the hole to reduce unintended bycatch. Selective snare setting or non-lethal snares (with cable stops) can also reduce non-target bycatch<span class="s1"><sup>1</sup></span>, which can be a common occurrence with snares. Trap lines should be checked daily, if possible, to insure traps are properly and continuously set and that caught animals are not subjected to prolonged suffering or injuries, especially if using non-lethal snares.</p><p class="p2">Of the 40 predator-made holes identified and filled in the experiment, a total of 20 successful re-digs and four unsuccessful re-digs occurred. There was a total of 14 holes filled or refilled with only dirt, 18 holes filled or refilled with dirt/cactus, and 15 holes filled or refilled with dirt/thorny brush, and 13 holes remaining at the end of the experiment for snare sets. Dirt alone was the least successful deterrent for predator re-dig activity; of 9/14 (64%) dirt-filled holes experienced successful re-dig attempts and 0/14 (0%) unsuccessful re-dig attempts. Although dirt/cactus-filled holes experienced one more successful re-dig attempt than dirt/thorny brush-filled holes (6/18 versus 5/15), both groups experienced the same statistical occurrence of successful re-dig attempts (33% success rate). Dirt/thorny brush-filled holes did, however, experience a slightly higher rate of unsuccessful re-dig attempts (11%) than that of dirt/cactus filled holes (13%). Evidence indicates that the addition of any deterring substrate (cactus or thorny brush) to filled holes reduced the rate of re-dig activity by half. It should be noted that cactus added as a hole filler may promote cactus growth along fence-lines, which may inhibit fence maintenance but could, if thick enough, also act as a natural succulent fire break in a wildfire situation. There was new cactus growth in some holes by the end of the study (within 39 days). Less penetrable filler such as razor wire, galvanized steel panel, or concrete may further deter predator re-dig activity, but is more costly and time-consuming.</p>								</div>
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									<h5 class="p1"><b>Table 1: Holes dimensions associated with evidence of various predators.</b></h5><p>The dimensions listed are in inches. The average is shown with the range shown parenthetically as (minimum – maximum). There is a significant overlap in hole dimensions among common predators (coyotes, bobcats, raccoons) and non-target species (javelina). * Indicates no range is provided because there was only one sample.</p><div><b><img decoding="async" class="alignnone wp-image-6625 size-large" src="https://theranchtx.us/wp-content/uploads/2024/09/Screenshot-2024-09-21-at-1.38.10 PM-1024x614.png" alt="" width="1024" height="614" /></b></div>								</div>
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									<h5 class="p1">Literature Cited</h5><ol><li style="list-style-type: none;"><ol class="ol1"><li class="li1">Boddicker ML. 1982. Snares for predator control.<i> Proceedings Tenth Vertebrate Pest Conference</i> pp50–54.</li><li class="li1">Dreibelbis JZ, Melton KB, Aguirre R, Collier BA, Hardin J, Silvy NJ, Peterson MJ. 2008. Predation of Rio Grande Wild Turkey Nests on the Edwards Plateau, Texas. <i>The Wilson Journal of Ornithology </i>120(4):906–910.</li><li class="li1">Guthery FS, Beasom SL. 1977. Responses of Game and Nongame Wildlife to Predator Control in South Texas. <i>Journal of Range Management</i> 30(6):404–409.</li><li class="li2"><span class="s1">Rollins DA, Carroll JP. 2001. Impacts Of Predation On Quail. </span><span class="s2"><i>The Role of Predator Control as a Tool in Game Management Proceedings of a Symposium </i>pp84–101<i>.</i></span></li><li class="li1">Texas A&amp;M AgriLife Extension Service–Wildlife Services. 2022. <a href="https://sanangelo.tamu.edu/files/2023/04/managing-coyotes-with-snares.pdf.">Managing Coyotes With Snares.</a>  Accessed July 9, 2024.</li><li class="li3"><span class="s2">Watine LN, Giuliano WM. 2017. Factors Determining Coyote (Canis latrans) Diets. <i>Open Journal of Ecology</i> 7:650–666.</span></li></ol></li></ol>								</div>
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		<p>The post <a href="https://theranchtx.us/assessing-various-predator-crossing-deterrents-for-fence-line-management-on-a-white-tailed-deer-ranch-in-southern-texas/">Assessing Various Predator Crossing Deterrents for Fence Line Management on A White-Tailed Deer Ranch in Southern Texas</a> appeared first on <a href="https://theranchtx.us">TheRanch at Camp Ka Hui Ana</a>.</p>
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		<title>Bison in Texas: Native or Exotic?</title>
		<link>https://theranchtx.us/bison-in-texas-native-or-exotic/?utm_source=rss&#038;utm_medium=rss&#038;utm_campaign=bison-in-texas-native-or-exotic</link>
		
		<dc:creator><![CDATA[Chase Nunez MS PhD]]></dc:creator>
		<pubDate>Sun, 25 Aug 2024 20:17:14 +0000</pubDate>
				<category><![CDATA[Bison]]></category>
		<category><![CDATA[Exotics]]></category>
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					<description><![CDATA[<p>Texas is known for its iconic white-tailed deer, making it a hub for hunting enthusiasts. What you might not know is that effective deer management relies on understanding the animals, their requirements, and their struggles. A balance of genetics, age, and nutrition are required to grow healthy deer with big antlers. While a ranch cannot necessarily change the existing genetics or control the age of the deer their neighbors harvest, they can improve the availability of nutritious feed. Spring and summer nutritional intake are also important for both does and bucks alike, making good year-round nutrition a vital aspect of maintaining a healthy deer herd.</p>
<p>The post <a href="https://theranchtx.us/bison-in-texas-native-or-exotic/">Bison in Texas: Native or Exotic?</a> appeared first on <a href="https://theranchtx.us">TheRanch at Camp Ka Hui Ana</a>.</p>
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									<p class="p1">When one thinks of the old west, the mind’s eye may see cowboys and Indians in a gunfight, or maybe the transcontinental railroad cutting across the country, or a prospector panning for gold… but I think of bison. The great beasts of the plains, once millions strong in herds a mile wide that continued onward as steady as time, and nearly lost to the hands of greed and negligence. The dismal history of bison prefaced, what is often considered, one of the great conservation successes and led to bison becoming the national mammal of United States of America. But were those conservation efforts to save this iconic species actually successful– it depends on the perspective and definition of success.</p><p class="p1">North American plains bison (<i>Bison bison</i>) went through an extreme genetic bottleneck when the population was decimated by indiscriminate commercial hunting and disease epidemics introduced by domesticated cattle. The remaining bison were protected, and the species recovered before physical extinction, but random cross-breeding and intentional efforts to hybridize cattle and bison by ranchers and wildlife managers became rampant. Cattle ranchers were hybridizing bison and cattle to produce a “beefalo” that was heartier and more durable than cattle but with a higher quality beef than bison. When these hybrids bred back to bison, they became visibly indistinguishable from pure bison<span class="s1"><sup>1</sup></span>. As a result, wildlife managers also contributed to spread hybridized bison, often unintentionally by integrating hybridized bison into pure bison herds but occasionally intentionally to bolster bison genetics against diseases without changing the physical appearance. After generations of visually indistinguishable hybrid bison contributing to the gene pool of the population, it was thought there were only a few genetically pure herds remaining such as the Yellowstone, Custer, Wind Cave, and Castle Rock (Vermejo) Herds. Unfortunately, with the use of advanced genetic sequencing techniques, a recent study from Texas A&amp;M University indicated that even the genetically pure herds are in fact infested with cattle genes<span class="s1"><sup>3</sup></span>. This essentially means that pure North American plains bison are genetically extinct, including those bison in the Texas state bison herd at the Caprock Canyons State Park. So was the conservation effort to save bison a success? Genetically, no. Ecologically, yes, because although the remaining bison are not 100% pure, they appear as if they were pure and are still on the landscape fulfilling the ecological role. So, if we, as wildlife managers, consider the saving of bison a success, do we consider them native wildlife or exotic livestock?</p><p class="p2">At a national level, bison are considered a wildlife resource that the United States Department of the Interior actively works to restore on Native American reservation and national forest/park land<a href="https://www.doi.gov/blog/15-facts-about-our-national-mammal-american-bison#:~:text=The%20Department%20of%20the%20Interior%20collaborates%20with%20other%20federal%2C%20Tribal,public%20to%20our%20national%20mammal"><span class="s1"><sup>5</sup></span></a>. At the state level, only six states (Alaska, Arizona, Montana, Utah, South Dakota, and Wyoming<a href="https://www.boone-crockett.org/big-game-profiles-r-american-bison"><span class="s1"><sup>2</sup></span></a>) recognize bison as a game animal with regulated seasons and bag limits. In Texas, however, similar to many of the remaining 44 states, bison are considered livestock, regulated by the states’ livestock health agencies (i.e.- Texas Animal Health Commission) and propagated by private ranches for meat, fiber, hunting, or other purposes<span class="s1"><sup>3</sup></span>. Bison, as “exotic livestock” in Texas, are not subject to hunting regulatory seasons, methods of take, or bag limits. The harvest of bison is legally equivalent to butchering a domestic livestock animal (cow, sheep, goat, hog, etc.), and the live sale and/or movement of bison is regulated similarly to domestic livestock, albeit with less disease surveillance (i.e.- trichomoniasis testing exemption). Despite these considerations, there is a heritage wild bison herd managed at the Caprock Canyons State Park in Briscoe County, Texas– the Official State Bison Herd of Texas.</p><p class="p1">The animals belonging to the Texas State Bison herd are descendants of the last wild Texas bison known to survive, which were rescued, adopted, and raised by Molly and Charles Goodnight in the late 1870’s. The handful of young bison were the genesis of the private Goodnight Bison Herd on the Goodnight’s JA Ranch in Armstrong County. Decades later, the bison herd was donated by the JA Ranch to the state of Texas and moved to the Caprock Canyons State Park in 1997 to become what is now the Texas State Bison Herd<a href="https://tpwd.texas.gov/state-parks/caprock-canyons/bison/story"><span class="s1"><sup>4</sup></span></a>. Occasionally these animals are rounded up for genetic culling and general health checks to keep the herd as healthy and genetically robust as possible<a href="https://tpwd.texas.gov/state-parks/caprock-canyons/bison/story"><span class="s1"><sup>4</sup></span></a>, but for the most part, the herd is managed as a wildlife resource at the park.</p><p class="p1">All this circles back to show the answer to the question, <i>“Are bison native or exotic to Texas?”,</i> is complicated and not-at-all straight-forward. From a cultural perspective, bison are the National Mammal of the United States and a religious symbol to many Native American cultures. From a historical perspective, the bison range included Texas and bison were never completely physically exterminated from the landscape. From a genetic perspective, pure American plains bison are likely genetically extinct. And from a regulatory perspective, bison are exotic hoof-stock in Texas.</p>								</div>
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									<ol class="ol1"><li class="li1"><p class="p1">Literature Cited:</p><ol class="ol1"><li class="li2"><span class="s2">American Bison Society. 1908. <i>Annual report of the American Bison Society 1905–1908</i>. vol. [1</span><span class="s3"><sup>st</sup></span><span class="s2">]-2</span><span class="s3"><sup>nd</sup></span><span class="s2">. </span></li><li class="li1">Boone and Crockett Club. 2020. <a href="https://www.boone-crockett.org/big-game-profiles-r-american-bison">Big Game Profiles- American Bison.</a> Accessed on July 9, 2024.</li><li class="li1">Stroupe S, Forgacs D, Harris A, Derr JN, Davis BW. 2022. Genomic evaluation of hybridization in historic and modern North American Bison (Bison bison). <i>Scientific Reports</i> 12:6397.</li><li class="li1">Texas Parks and Wildlife Department.  <a href="https://tpwd.texas.gov/state-parks/caprock-canyons/bison/story">Caprock Canyons State Park &amp; Trailway.</a> Accessed on July 9, 2024.</li><li class="li3"><span class="s5">United States Department of the Interior. 2022. <a href="https://www.doi.gov/blog/15-facts-about-our-national-mammal-american-bison#:~:text=The%20Department%20of%20the%20Interior%20collaborates%20with%20other%20federal%2C%20Tribal,public%20to%20our%20national%20mammal">15 Facts About Our National Mammal: The American Bison.</a> Accessed on July 9, 2024.</span></li></ol></li></ol>								</div>
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		<p>The post <a href="https://theranchtx.us/bison-in-texas-native-or-exotic/">Bison in Texas: Native or Exotic?</a> appeared first on <a href="https://theranchtx.us">TheRanch at Camp Ka Hui Ana</a>.</p>
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