日本高山沼地池中蠓幼虫和蜻蜓捕食的空间变化

H. Togashi, Takao Suzuki, J. Urabe
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引用次数: 2

摘要

山地沼泽是日本高山和亚高山地区的典型景观组成部分,经常有数百个大小不一的水池。在这些水池中,手蛾科(双翅目)的幼虫以及其他水生昆虫和浮游动物占主导地位(KURASAWA et al. 1982, IWAKUMA 1995)。然而,这种幼虫的丰度和物种组成在不同的池塘之间差异很大,即使在同一沼泽内(KURASAWA et al. 1982; UENO & IWAKUMA 1996)。这些空间变化提供了一个独特的机会来研究决定摇尾蛾幼虫丰度及其群落组成的因素。一些研究表明,淡水中摇尾蛾幼虫的群落结构受多种因素的影响,如pH值(WALKER et al. 1985, KRATZ et al. 1994)、大型植物的丰度和组成(CARDINALE et al. 1997, BRoDERSEN et al. 2001)、生产力(SAETHER 1979, PERRIN & RrcHARDSON 1997)、产卵和定植率(ToKESHI & TowNSEND 1987)和捕食(ThoRP & CoTHRAN 1984, WALDE & DAVIES 1984, JoHNSON et al. 1987, GoYKE & HERSHEY 1992, DIEHL 1995)。然而,山地沼地绿腹虫幼虫群落结构的影响因素尚不清楚。在淡水生境中,捕食是决定水生生物丰度和组成的关键因素(DIEHL 1995, WELLBORN et al. 1996)。在日本东北部早山的Shibakusa-Daira沼地中,与其他沼地一样,池与池之间手摇蝇幼虫的丰度和组成也不同(KuRASAWA et al. 1982, UENO & IWAKUMA 1996)。这些池塘里没有鱼,但有几种掠食性动物,包括蝾螈(Hynobious nigrescens)和桤木蝇(Sialis tohokuensis)的幼虫,豆娘(Lestes sponsa)和蜻蜓(Aeshna juncea andA)的若虫。nigrojlava)。然而,蝾螈幼虫只在春末夏初出现在这些池塘里,而红木蝇和豆豆蝇的数量全年都非常有限。因此,蜻蜓若虫是Shibakusa-Daira池塘中最丰富的捕食者。峨眉山属植物广泛分布于欧亚大陆至北美洲,而黑岩属植物仅产于日本。众所周知,这种昆虫的幼虫以双翅目昆虫为食,包括衣纲昆虫的幼虫(JOHNSON 1985, JOHANSSON 1993);因此,我们假设Aeshna的捕食是Shibakusa-Daira池中绿虫幼虫丰度和组成差异的因素之一。我们通过在现场实验中操纵Aeshna丰度来验证这一假设。
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Spatial variations in chironomid larvae and dragonfly predation in pools on a Japanese high mountain moor
Mountain moors, a typical landscape component of alpine and subalpine areas in Japan, frequently feature hundreds of pools ofvarious sizes. In these pools, larvae ofchironomidae (Diptera) are predominant, along with other aquatic insects and zooplankton (KURASAWA et al. 1982, IWAKUMA 1995). However, the abundance of such larvae and the species composition vary highly among pools even within the same moor (KURASAWA et al. 1982, UENO & IWAKUMA 1996). These spatial variations provide a unique opportunity to examine the factors that determine abundance of chironomid larvae and compositions o f their communities. Several studies have shown that community structures of chironomid larvae in fresh water are affected by various factors such as pH (WALKER et al. 1985, KRATZ et al. 1994), abundance and composition of macrophytes (CARDINALE et al. 1997, BRoDERSEN et al. 2001), productivity (SAETHER 1979, PERRIN & RrcHARDSON 1997), oviposition and colonization rates (ToKESHI & TowNSEND 1987), and predation (ThoRP & CoTHRAN 1984, WALDE & DAVIES 1984, JoHNSON et al. 1987, GoYKE & HERSHEY 1992, DIEHL 1995). However, little is known about the factors that determine community structures of chironornid larvae in mountain moors. In freshwater habitats, predation is crucial in determining abundance and composition of aquatic organisms (DIEHL 1995, WELLBORN et al. 1996). In the Shibakusa-Daira moors of the Zao Mountains in northeastem Japan, the abundance and composition of chironomidae larvae differ from pool to pool as they do in other moors (KuRASAWA et al. 1982, UENO & IWAKUMA 1996). These poo1s contain no fish but have several predatory animals, including the larvae of salamanders (Hynobious nigrescens) and alderflies (Sialis tohokuensis), and the nymphs of damselflies (Lestes sponsa) and dragonflies (Aeshna juncea andA. nigrojlava). Salamander larvae appear in these pools only in late spring to early summer, however, and the populations o f alderflies and damselflies are highly limited throughout the year. Thus, dragonfly nymphs are the most abundant predators in the pools at the Shibakusa-Daira. Aeshnajuncea are widely distributed from Eurasia to North America, but A. nigrojlava is endernic to Japan. Larvae o f this g en us are known to prey o n Diptera, including chironornid larvae (JOHNSON 1985, JOHANSSON 1993); therefore, we hypothesized that predation by Aeshna is one of the factors differentiating the abundance and composition of chironornid 1arvae among the Shibakusa-Daira pools. We tested this hypothesis by manipulating Aeshna abundance in a field experirnent.
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