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Thomas WH 《Environmental management》2010,45(1):82-92
It has been proposed that indigenous societies can be models for the conservation of biodiversity. However, attempts at implementing
conservation-based development plans are being judged failures. In this article, I argue that these failures can be addressed
by translating indigenous knowledge into context that is mutually intelligible to both indigenous people and conservation
biologists. Drawing on sixteen months of ethnobiological fieldwork, this article uses indigenous knowledge to describe the
relationship of traditional life to biodiversity for the Hewa of Papua New Guinea’s Central Range. The island of New Guinea
is one of the planet’s last bastions of cultural and biological diversity. Using birds as an indicator of diversity, I argue
that more productive conservation policies will emerge when indigenous activities are viewed not as vehicles for establishing
equilibrium with the environment, but as a source of ecological disturbance. Although Hewa traditions currently play a significant
role in shaping this biologically diverse environment, their lifestyle is not necessarily a template for sustainability in
the future. 相似文献
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Z. G. Prishutova 《Russian Journal of Ecology》2010,41(1):55-59
Vegetation was considerably trampled throughout Vodnyi Island in the Rostovskii Nature Reserve in 2007 because of a high pasture
load due to feral horses (0.15 horses/ha). Calculation of the food resources on the island, with its protection as part of
a nature reserve taken into account, has shown that the herd size is 3.5 times larger than the maximum allowable value. 相似文献
356.
Secondary pest outbreak is a counterintuitive ecological backlash of pesticide use in agriculture that takes place with the increase in abundance of a non-targeted pest species after pesticide application against a targeted pest species. Although the phenomenon was well recognized, its alternative causes are seldom considered. Outbreaks of the southern red mite Oligonychus ilicis are frequently reported in Brazilian coffee farms after the application of pyrethroid insecticides against the coffee leaf miner Leucoptera coffeella. Selectivity favoring the red mite against its main predatory mites is generally assumed as the outbreak cause, but this theory has never been tested. Here, we assessed the toxicity (and thus the selectivity) of deltamethrin against both mite species: the southern red mite and its phytoseid predator Amblyseius herbicolus. Additionally, behavioral avoidance and deltamethrin-induced hormesis were also tested as potential causes of red mite outbreak using free-choice behavioral walking bioassays with the predatory mite and life-table experiments with both mite species, respectively. Lethal toxicity bioassays indicated that the predatory mite was slightly more susceptible than its prey (1.5×), but in more robust demographic bioassays, the predator was three times more tolerant to deltamethrin than its prey, indicating that predator susceptibility to deltamethrin is not a cause of the reported outbreaks. The predator did not exhibit behavioral avoidance to deltamethrin; however insecticide-induced hormesis in the red mite led to its high population increase under low doses, which was not observed for the predatory mite. Therefore, deltamethrin-induced hormesis is a likely cause of the reported red mite outbreaks. 相似文献
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F.L. Voelz S.I. Weinberg B.G. Gower 《Journal of the Air & Waste Management Association (1995)》2013,63(12):935-942
Gross average automotive exhaust emissions data collected by the Atlantic Richfield Clean Air Caravan during the summer of 1970 showed only slight geographical variations when the specific makes were ignored. When considering specific makes, significant differences were found on an average emissions basis. Vehicle population—emission distributions showed wide variations in the 50% population levels and in the percent of vehicles with emissions greater than specified values. Hydrocarbon (HC) and carbon monoxide (CO) data are given on a gross basis for the 1970, 1968-69, 1966-67, and pre-1966 model year group vehicles. Average HC and CO emissions and vehicle population-Idle emissions distribution curves are included for specific make vehicles in selected areas. 相似文献