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Directing nest site selection of least terns and piping plovers.

机译:指导最少燕鸥和管道pl的巢址选择。

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Endangered Interior Least Terns (Sterna antillarum athalassos) and threatened Piping Plovers (Charadrius melodus) nest in Nebraska at gravel mines where they are vulnerable to disturbance and nest loss. Conflicts occur when their nesting and protected status delay mining activities. The possibility of shifting nesting from active to inactive mining areas by using a deterrent (mylar flagging), an attractant (gravel and driftwood spread on bare sand), and a control (untreated sand) was evaluated. Experimental plots (mean 0.36 ha) were established at 18 different gravel mines, twelve in 2000 and seven (one repeat) in 2001 along the Platte and Elkhorn rivers prior to nesting season. Of 117 tern nests, 73% were in attractant, 2% in deterrent, and 26% in control plots. Of 23 plover nests, 61% were in attractant, 9% in deterrent, and 30% in control. Colonies used plots containing less vegetation and more driftwood than unused plots. Within control plots, both tern and plover nests were Surrounded by more large (>15 min) gravel and less coarse sand than was available at random points. Within attractant plots, substrate at the nest did not differ from random points. In all plots, Least Tern nests were more likely to have driftwood by the nest than was available at random points. Hatching rates did not differ between attractant and control plots. To attract Least Terns and Piping Plovers, sand covered with 15% small gravel, 5-10% large gravel, 3% vegetation, and about ten pieces driftwood/1,000 m2 was found to be effective. As deterrents, mylar streamers 7 in long, 30 min wide, and 0.025 min thick, attached to I in poles arranged in a 7 in grid were used. The combination of attractant and deterrent treatments provided a mechanism to protect nesting birds and avoid conflicts.
机译:濒临灭绝的内陆最小燕鸥(Sterna antillarum athalassos)和濒临灭绝的管道采伐者(Charadrius melodus)在内布拉斯加的砾石矿中筑巢,他们很容易受到干扰和筑巢损失。当冲突的嵌套和受保护状态延迟采矿活动时,就会发生冲突。通过使用威慑剂(聚酯薄膜标记),引诱剂(碎石和浮木散布在裸露的沙子上)和对照(未处理的沙子)上,评估了将筑巢从活动矿区转移到非活动矿区的可能性。在筑巢季节之前,沿着普拉特河和埃尔克霍恩河在18个不同的砾石矿山上建立了试验区(平均0.36公顷),2000年建立了12个,2001年建立了七个(重复一次)。在117个燕窝中,引诱剂占73%,威慑作用占2%,对照区占26%。在23个巢中,引诱物占61%,威慑物占9%,对照物占30%。殖民地使用的土地比未使用的土地包含更少的植被和更多的浮木。在控制区内,燕鸥巢和over巢都被比随机点更大的(> 15分钟)砾石和更少的粗砂包围。在引诱地块中,巢穴的底物与随机点没有差异。在所有样地中,与随机点相比,最少燕鸥的巢旁更有浮木的可能。引诱区和对照区的孵化率没有差异。为了吸引最小的燕鸥和管道爱好者,发现用15%小砾石,5-10%大砾石,3%植被和大约十块浮木/ 1,000平方米覆盖的沙子是有效的。作为阻吓剂,使用了长,宽30分钟,厚0.025分钟的聚脂薄膜拖缆7,该拖缆以7英寸的网格排列固定在I极上。引诱和威慑措施的结合提供了一种保护筑巢鸟类和避免冲突的机制。

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