首页> 外文学位 >False map, spiny softshell and smooth softshell turtle nest and nest-site habitat characteristics along the lower stretch of the Missouri National Recreation River in South Dakota.
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False map, spiny softshell and smooth softshell turtle nest and nest-site habitat characteristics along the lower stretch of the Missouri National Recreation River in South Dakota.

机译:在南达科他州密苏里国家休闲河下游,错误的地图,多刺的软壳和光滑的软壳海龟巢以及巢穴栖息地的特征。

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摘要

Little is known about the ecology and reproductive habits of turtles in South Dakota. The spiny softshell (Apalone spinifera) and smooth softshell (A. mutica) are listed as species of concern in South Dakota and the false map turtle (Graptemys pseudographica ) is listed as state threatened. Information relating to habitat and nest site characteristics is needed to form sound management plans.;Surveys were conducted for turtle nests along the Missouri National Recreation River from just above Lewis and Clark Lake (river mile (RM) 835) to Ponca State Park (RM 753) in 2006 and 2007. Turtle nests were located by walking shorelines and sandbars while searching for tracks, scrapes and nesting turtles. Once located, each nest was identified to genus and recorded on global positioning system (GPS). Nest characteristics taken were number of eggs, egg size, depth to top egg in nest, and distance from water. To determine habitat variables female turtles were selecting for, I examined nest site, on-site location and off-site location land cover classification and habitat vegetation variables including type, height, and percent cover. Substrate composition and debris were also assessed.;Turtles were first observed nesting in 2006 on 6 June and nesting continued until 23 July 2006. During 2007 the first nest was found on 28 May and the last nest located was 28 June. In 2007, 230.5 hours were spent searching sandbars resulting in a detection rate of one nest every 5.5 hours. I found 17 false map and 45 softshell nests intact and excavated them for measurements.;The mean number of eggs in an Apalone sp. clutch was 14.61, mean egg diameter was 23.97 mm, and mean depth to the top egg was 9.09 cm. The mean number of eggs in a G. pseudogeographica nest was 10.5, mean egg width was 23.16 mm, mean length was 34.42 mm + 0.210 and the mean depth to the top egg was 9.95 cm. The mean straight line distance to water traveled by nesting Apalone sp. was 61.27 m and the mean straight line distance to water traveled by nesting G. pseudogeographica was 54.24 m. There was no difference in straight line distance to water between Apalone sp. and G. pseudogeographica (p = 0.552, t = 0.601, df = 36.47).;There was a difference between slopes of man-made sandbars and natural sandbars (p = 0.003, t = -3.699, df = 13.35). When the mean slope of a sandbar was compared to the mean straight line distance from nest to water on the same sandbar Apalone sp. had a R2 value of 0.1487 (n = 13) and G. pseudogeographica had an R 2 value of 0.2471 (n = 7).;In 2007, the depredation rate of monitored nests was 36%. There was no depredation of nests on the man-made sandbars. Straight line distance to the water and habitat characteristics at the nest site had no effect on nest depredation rates of located nests. I found 184 depredated nests (175 Apalone sp. and nine G. pseudogeographica).;Apalone sp. nested exclusively in bare sandy areas while G. pseudogeographica tolerated sparse vegetation around the nest site. A nest-site selection model was constructed using a matched-pair stepwise logistic regression at the off-site level for Apalone sp. using the habitat variables that had a difference (p ≤ 0.05) between the nest site and the off-site. The habitat variables used included: terrestrial herbaceous vegetation (p = 0.046), woody vegetation (p = 0.008), woody vegetation stem number (p = 0.020), mean vegetation height (p = 0.032), max vegetation height (p = 0.025) and leaf debris (p = 0.046). The final calculated model included max vegetation height and leaf debris (p = 0.007, McFadden Rho 2 = 0.123). A habitat nest-site selection model could not be constructed for Apalone sp. at the on-site level or for G. pseudogeographica at either the on-site or off-site level because there were no differences between habitat variables. Spatial analyses of the depredated nests at RM 804.5 suggest those turtle nests are clustered in bare open sand. Three Apalone sp. nests hatched before surveys were completed in 2007. Based on this data, an estimate incubation length for Apalone sp. turtles was 70--71 days. Vegetation surrounding the nest site may have decreased incubation length by causing an increase in nest cavity temperature.;Both Apalone sp. and G. pseudogeographica utilize natural and man-made sandbar habitat for nesting. However, natural nesting beaches are being reduced at a rapid pace, and man-made sandbars may not provide the most ideal conditions for hatchlings and adult turtles. Turtle populations along the Missouri National Recreation River are at risk for further decrease if management and conservation efforts are not focused on providing quality nesting habitat.
机译:关于南达科他州海龟的生态和生殖习性知之甚少。在南达科他州,有刺的软体动物(Apalone spinifera)和光滑的软体动物(A. mutica)被列为关注物种,而假地图龟(Graptemys pseudographica)被列为受威胁国家。需要与栖息地和巢址特征有关的信息来制定完善的管理计划。进行了密苏里州国家休闲河沿线的龟巢调查,该河道从刘易斯和克拉克湖(RM 835)到庞卡州立公园(RM) 753)在2006年和2007年。在搜寻足迹,刮es和筑巢龟时,通过走过海岸线和沙洲找到了龟巢。一旦定位,每个巢都被识别为属并记录在全球定位系统(GPS)上。采取的巢特征是卵的数量,卵的大小,巢中至顶部卵的深度以及与水的距离。为了确定雌性海龟的栖息地变量,我检查了巢穴,现场位置和异地位置的土地覆盖分类以及栖息地植被变量,包括类型,高度和覆盖率。还评估了基质的成分和碎片。2006年,首次观察到龟在6月6日筑巢,筑巢一直持续到2006年7月23日。2007年,在5月28日发现了第一个巢,最后一个巢是6月28日。 2007年,花了230.5个小时搜索沙洲,因此每5.5个小时发现一个巢的比率就很高。我发现完整的17个虚假图和45个软壳巢被挖出以进行测量。离合为14.61,平均蛋径为23.97毫米,到顶部蛋的平均深度为9.09厘米。假地理鸟巢中的平均卵数为10.5,平均卵宽为23.16 mm,平均卵长为34.42 mm + 0.210,到顶卵的平均深度为9.95 cm。嵌套Apalone sp。到水的平均直线距离。筑巢假地理距离水的平均直线距离为61.27 m,54.24 m。 Apalone sp。到水的直线距离没有差异。人工沙洲和天然沙洲的坡度之间存在差异(p = 0.003,t = -3.699,df = 13.35); G. pseudogeographica(p = 0.552,t = 0.601,df = 36.47)。将沙洲的平均坡度与同一个沙洲上从巢到水的平均直线距离进行比较时。 R2值为0.1487(n = 13),假山G的R 2值为0.2471(n = 7)。;2007年,监测巢的折旧率是36%。人造沙洲上没有巢穴。到巢点水位和栖息地特征的直线距离不会影响巢穴的退化率。我发现了184个过时的巢(175个Apalone sp。和9个G. pseudogeographica)。仅在裸露的沙质区域筑巢,而伪地理学(G. pseudogeographica)忍受巢穴周围稀疏的植被。使用Apalone sp在场外级别使用匹配对逐步逻辑回归构建巢位选择模型。使用栖息地与异地之间的差异(p≤0.05)的栖息地变量。使用的栖息地变量包括:陆生草本植被(p = 0.046),木质植被(p = 0.008),木质植被茎数(p = 0.020),平均植被高度(p = 0.032),最大植被高度(p = 0.025)和叶片碎片(p = 0.046)。最终计算出的模型包括最大植被高度和叶片碎片(p = 0.007,McFadden Rho 2 = 0.123)。无法为Apalone sp。构建栖息地巢穴选择模型。因为在生境变量之间没有差异,所以在实地或在实地或非实地的G. pseudogeographica都可以。对过时的巢穴进行空间分析(RM 804.5)表明,这些龟巢聚集在裸露的裸露沙子中。三个Apalone sp。巢于2007年完成调查之前孵化。基于此数据,Apalone sp。的估计孵化期。海龟是70--71天。巢穴周围的植被可能会导致巢穴温度升高,从而缩短孵化长度。 G. pseudogeographica和G. pseudogeographica利用天然和人造沙洲栖息地筑巢。但是,天然的筑巢海滩正在迅速减少,人造沙洲可能无法为孵化和成年海龟提供最理想的条件。如果管理和保护工作不着眼于提供优质的筑巢栖息地,密苏里国家休闲河沿岸的海龟种群将有进一步减少的危险。

著录项

  • 作者

    Dixon, Laura A.;

  • 作者单位

    South Dakota State University.;

  • 授予单位 South Dakota State University.;
  • 学科 Agriculture Wildlife Conservation.;Biology Ecology.
  • 学位 M.S.
  • 年度 2009
  • 页码 112 p.
  • 总页数 112
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 生态学(生物生态学);
  • 关键词

  • 入库时间 2022-08-17 11:37:37

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