三种新热带爬行动物的睡眠地点保真度

Spring 2021 Pub Date : 2021-04-01 DOI:10.33256/HB155.811
Oliver Thomas, G. Mangini, Juan Gualinga
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引用次数: 0

摘要

迄今为止研究的一种动物已经表现出睡眠或类似睡眠的行为(Tobler, 2000)。睡眠有助于多种过程,包括细胞和内分泌系统的恢复,通过学习,记忆和能量保存(Mignot, 2008;Libourel & Herrel, 2016)。与此同时,睡眠也可能带来风险,因为动物在不活动的时候可能会被捕食(Amlaner & Ball, 1983)。无论其功能如何,睡眠是动物行为中最突出的行为之一,因此可能是一种动态响应和适应不同环境变量的行为(Tobler, 2000)。睡眠地点的选择必须在获得睡眠的好处,同时避免捕食的重要作用(Amlaner & Ball, 1983)。这可能受到微生境偏好、保护免受捕食者或暴露的需要以及留在领地内以避免竞争的影响(Christian等人,1984;Clark & Gillingham, 1990)。因此,一旦被选中,睡眠部位可能会维持数天、数周或更长时间,以保持这些益处(González-Zamora等人,2015)。然而,迄今为止,关于睡眠地点偏好或地点保真度的研究主要集中在恒温动物(哺乳动物和鸟类)身上,而不是爬行动物、两栖动物、鱼类或无脊椎动物等变温动物(Amlaner & Ball, 1983;Campbell & Tobler出版社,1984;Christian et al., 1984;Clark & Gillingham, 1990;Hartse, 1994)。具体来说,在爬行动物中,睡眠地点在蜥蜴中被广泛记录,包括一些亚马逊物种,如斑点蜥蜴、粗皮蜥蜴和横纹蜥蜴。然而,关于其他爬行动物和两栖动物的信息却少得多(Clark & Gillingham, 1990;维特等人,2002;Vitt et al., 2003a;Vitt et al., 2003b;Poche et al., 2005)。本研究报告了两种蜥蜴Enyalioides latieps (Guichenot, 1855)和Anolis fuscoauratus D 'Orbigny(1937)以及一种两栖动物蟾蜍Rhinella margaritifera (Laurenti, 1768)的睡眠地点保真度。为了收集数据,我们于2019年6月至8月期间在厄瓜多尔Sucumbíos(0°26 ' 18.47 " S, 76°16 ' 45.11 " W)的萨尼保护区的露营区进行了白天和夜间的视觉接触调查。萨尼保护区的栖息地主要是陆地森林,igapó(黑水泛滥森林)和varzea(白水泛滥森林)与Challuacocha泻湖及其周围的芦苇和草位于保护区生态周围(Hollamby, 2010)。在轮流的基础上,在不同的日子对6条小径进行了调查。在7月10日和7月17日,我们分别记录了两种植物的睡眠情况。睡眠是通过行为指标来确定的,比如我们到达时闭上眼睛,缺乏逃跑行为,或者在报告的睡眠活动模式之外观察的时间。在营地中,我们从7月19日起在同一地点记录了一只褐口吸螨个体返回睡眠。我们将标记带放置在离白蛉和白蛉睡眠地点几米远的地方,作为警告,这样我们就可以在靠近时慢慢靠近,同时也不会引起人们对特定地点的注意。然后,我们从2019年7月24日至2019年8月4日每天访问这些标记站点,并从2019年7月19日至2019年8月4日每天访问fuscoauratus站点(在营地)。我们没有在周一参观任何一个景点,因为我们不在保护区。由于天气恶劣,我们在8月1日和3日无法到达E. laticeps和R. margaritifera的地点,但我们仍然可以观察到A. fuscoauratus,因为这是在营地内。在每次访问中,我们记录了这些个体在这些地点的存在或不存在。为了描述用于睡眠的微栖息地的特征,我们拍摄了每个地点(图2A, 3A, 4A),并在每个情况下测量了距离地面的高度和距离小径的距离(如适用)。没有捕获动物,因此没有收集形态计量数据。根据它们的大小,这三个个体都被认为是成年人,每个个体都有独特的颜色图案,使我们能够在连续的场合自信地认出同一个体。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Sleeping site fidelity in three neotropical species of herpetofauna
A animal species studied to date have shown sleep or sleep-like behaviour (Tobler, 2000). Sleep aids in a variety of processes including recovery of cellular and endocrine systems through to learning, memory and energy conservation (Mignot, 2008; Libourel & Herrel, 2016). At the same time, periods of sleep could present risks as an animal may be exposed to predation while inactive (Amlaner & Ball, 1983). Regardless of its functions, sleep is among the most prominent of animal behaviours and as such is likely to be a behaviour that responds dynamically and adaptively to different environmental variables (Tobler, 2000). Sleeping site selection must play an important role in obtaining the benefits of sleep while avoiding predation (Amlaner & Ball, 1983). It is likely influenced by microhabitat preferences, the need for protection from predators or exposure, and remaining within territories to avoid competition (Christian et al., 1984; Clark & Gillingham, 1990). Thus, once selected, a sleeping site may be maintained through days, weeks, or longer, to retain these benefits over time (González-Zamora et al., 2015). However, to date studies of sleeping site preferences or site fidelity have focused mainly on endotherms (mammals and birds) rather than ectotherms such as reptiles, amphibians, fishes or invertebrates (Amlaner & Ball, 1983; Campbell & Tobler, 1984; Christian et al., 1984; Clark & Gillingham, 1990; Hartse, 1994). In reptiles specifically, sleeping sites have been recorded widely in anoles, including some Amazonian species such as Anolis punctatus, Anolis trachyderma and Anolis transversalis. However, there is far less information for other reptiles and amphibians (Clark & Gillingham, 1990; Vitt et al., 2002; Vitt et al., 2003a; Vitt et al., 2003b; Poche et al., 2005). Here we report sleep site fidelity for two species of lizard Enyalioides laticeps (Guichenot, 1855) and Anolis fuscoauratus D’Orbigny, 1937 and one amphibian species, the toad Rhinella margaritifera (Laurenti, 1768). To gather data, we undertook day and night-time visual encounter surveys between June and August 2019 in the camping area of the Sani Reserve, Sucumbíos, Ecuador (0° 26’ 18.47” S, 76° 16’ 45.11” W). The habitat in the Sani Reserve is a mixture of mostly terra firme forest, igapó (blackwater flooded forest) and varzea (white water flooded forest) with the Challuacocha lagoon and its surrounding reeds and grasses located around the reserve’s ecolodge (Hollamby, 2010). Six trails were surveyed on separate days on a rotational basis. During these surveys we first recorded E. laticeps and R. margaritifera sleeping on 10th July, and recorded them again on 17th July. Sleeping was determined through behavioural indicators such as closed eyes upon our arrival, lack of escape behaviour, or time of observation outside the reported diel activity pattern. In the camp, we recorded an individual A. fuscoauratus that was returning to sleep in the same site from the 19th July. We placed flagging tape a few metres from the sleeping sites of E. laticeps and R. margaritifera as a warning so that we could approach slowly when nearby while also not drawing attention to the specific site. We then visited these flagged sites daily from 24th July 2019 to 4th August 2019 and the A. fuscoauratus site (in camp) from 19th July to 4th August 2019. We did not visit the any of the sites on Mondays, as we were not in the reserve. We were unable to reach the E. laticeps and R. margaritifera sites on the 1st and 3rd of August due to bad weather, but we could still observe A. fuscoauratus as this was within the camp. During each visit we recorded the presence or absence of the individuals at the sites. To characterise the microhabitats used for sleeping, we photographed each location (Fig. 2A, 3A, 4A) and in each case measured the height from the ground and distance from the trail where applicable. The animals were not captured so morphometric data was not collected. Based on their size, all three individuals were considered to be adults and each had unique colour patterns that allowed us to confidently recognise the same individual on successive occasions.
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