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51.
红茶菌是以糖茶水为主要原料,经微生物发酵后形成的一种功能性茶饮品。近年来,随着人们生活水平的提高和保健意识的增强,具有多种保健功效的红茶菌受到国内外研究者的广泛关注,其全球销售量也呈指数增长。本文重点梳理了红茶菌中的微生物组成及其共生关系,概括了原料、培养条件和菌种组成对红茶菌发酵的影响,并归纳了红茶菌在抗氧化、抑菌、护肝、提高免疫力和防癌抗癌方面的保健功能研究。红茶菌生产中,活性大分子的鉴定和形成机制、各菌种的益生效果、发酵罐水平的精准调控、产品稳定性提升等方面还需进行深入研究。另外,本文展望了红茶菌在多个领域的应用前景,以期为红茶菌工业化生产提供参考。 相似文献
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Fish functional diversity responses following flood pulses in the upper Paraná River floodplain 下载免费PDF全文
Matheus T. Baumgartner Anielly G. de Oliveira Angelo A. Agostinho Luiz C. Gomes 《Ecology of Freshwater Fish》2018,27(4):910-919
Flood pulses are the main force driving the dynamics of aquatic communities in floodplains. The responses of communities to environmental changes following flood pulses usually demand a time lag to appear and reach the climax. We assembled a data set of 16 years of fish samplings to assess the relationship between water level and four functional diversity measures, in the upper Paraná River floodplain. Specifically, we approached four aspects of each relationship between water level and functional diversity: nature (positive or negative), sensitivity (response intensity), responsiveness (response delay) and extent (response duration). The nature of the relationship between water level and functional diversity was positive in all cases. Functional richness (FRic) responded right after flood pulses, although with shorter extent. Abundance‐dependent functional measures (evenness—FEve; divergence—FDiv; and Rao's quadratic entropy—Rao's Q) presented delayed responses, reaching peaks more than 1.5 years after flood pulses. Significant effects of floods on fish functional diversity were observed for more than 3 years, although the highest functional diversity was observed with 1.8 years, on average. More importantly, flood pulses had no longer significant effects on functional diversity after 4 years. Regarding conservation strategies in regulated systems, flood events should occur every 2 or 3 years, with adequate timing (October‐November), intensity (up to 450 cm) and duration (at least 50 uninterrupted days). Intervals longer than 3 years or inadequate timing, intensity and duration could dramatically decrease functional diversity and compromise ecosystem services. 相似文献
54.
Freshwater fishes are threatened globally, and often too little is known about threatened species to effectively guide their conservation. Habitat complexity is linked to fish species diversity and persistence, and degraded streams often lack habitat complexity. Beaver Castor spp., in turn, have been used to restore streams and increase habitat complexity. The northern leatherside chub Lepidomeda copei is a rare, small‐bodied, drift‐feeding minnow that has anecdotally been observed to use complex habitats associated with beaver dams in the western United States. To investigate this anecdote, we conducted fish and habitat surveys, the latter focusing on quantifying habitat complexity, in a sub‐basin of the Upper Snake River Basin in the USA. Complementary generalised linear model and path analyses revealed that northern leatherside chub occurred more often at sites with complex streamflows, and streamflows were more complex when beaver dams were present and pools were deeper. Northern leatherside chubs were also more likely to occur when temperatures were warmer, aquatic macrophytes were abundant and stream channels were narrow and deep. The linkage between chubs, complex streamflows and beaver dams needs to be evaluated more broadly to completely understand its role in the rangewide status of the species. However, it does suggests that increased use of beaver reintroductions and dam analogues for stream restoration could be a boon for the northern leatherside chub, but such efforts should be monitored to determine their effectiveness to help adapt beaver‐based restoration approaches to best benefit the species. 相似文献
55.
Over that past decade, ecological restoration practices have expanded globally. However, the effectiveness of ecological restoration depends on the complex interactions of various natural and socioeconomic factors, about which there is limited scientific understanding and thus provides an important research frontier. This paper analyzed the relationship between regional scale vegetation restoration and the process of urbanization using the Loess Plateau of China as a case study. This region has experienced both rapid urbanization and a high number of vegetation restoration activities. Urbanization and vegetation restoration can be considered as extremes on the spectrum of environment preservation activities. Three separate spatial correlation analyses between urbanization and vegetation restoration were identified, resulting in: 1) insignificant correlations in saturated urban areas; 2) significant negative correlations in peri-urban areas; and 3) significant positive correlations in undeveloped areas. The relationship between urbanization and vegetation restoration is thus stage-dependent. Impacts of urbanization on vegetation degradation has improved but has not been fully addressed by large scale vegetation restoration. Regardless of whether the county or grid scale is used, peri-urbanization was found to be the critical factor affecting the effectiveness of vegetation restoration over both time and space. Therefore, peri-urbanized areas are viewed as priorities for improving the coupling of urban development and vegetation restoration. 相似文献
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2014—2015年对宣成到官庄境内似鮈生活的汀江河段进行实地考察和采样,结果表明该江段水温、溶解氧和pH分别在17.2~28.5℃、7.03~8.63 mg/L和6.75~6.83之间变化;似鮈喜欢栖息多砾石或沙石的环境,一般隐蔽在石缝里。汀江似鮈每年4—7月为繁殖期,产卵盛期为5—6月;性成熟年龄为1~2龄,体重在8.1~56.3 g之间;雌鱼怀卵量为213~550粒/尾,相对繁殖力为20~120粒/g·体重,成熟系数为1.07%~8.37%,雄鱼成熟系数为0.41%~4.85%;产沉性卵,深黄色,卵径为(0.762±0.015)mm。产卵场水深约1.5~2.5 m,溶解氧为7.85~8.41 mg/L,水温为18.6~26.7℃,pH在6.8~7.2之间,底质以沙砾为主。 相似文献
58.
通过混养生态系统模拟试验研究了紫贻贝(Grateloupia lanceolata)和披针形蜈蚣藻(Mytilus edulis)不同养殖密度组合下的生态混养状况。选取壳长(45.14±3.85)mm的紫贻贝和长度(62.48±7.38)mm的披针形蜈蚣藻,采用5种湿重配比进行混养实验,分别为G1(1∶0)、G2(1∶0.25)、G3(1∶0.5)、G4(1∶1)和G5(1∶2)。每种组合中紫贻贝密度均为0.63 ind·L~(-1),而披针形蜈蚣藻密度分别为0 g·L~(-1)、1.25 g·L~(-1)、2.5 g·L~(-1)、5 g·L~(-1)、10 g·L~(-1)。36 d后,G3组中紫贻贝特定生长率为(0.21±0.03)%·d-1,极显著高于其它混养组[(0.11±0.028)~(0.21±0.03)%·d-1,P0.01],而单养组的紫贻贝特定生长率仅为(0.063±0.022)%·d-1;G3组中披针形蜈蚣藻特定生长率为(0.96±0.20)%·d-1,极显著高于其它混养组[(0.62±0.16)~(0.96±0.20)%·d-1,P0.01]。G3组生态系统对营养盐(NO_3~--N、NO_2~--N、NH_4~+-N、PO3-4-P)的去除率分别达到(91.38±1.40)%、(96.79±1.97)%、(98.38±2.06)%、(96.86±3.16)%,显著高于G2组(P0.05),而与G4和G5组没有显著性差异(P0.05)。本研究结果表明,当紫贻贝与披针形蜈蚣藻湿重比为1∶0.5时,可以取得较好的生态效应。 相似文献
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60.
Luc Doyen Christophe Béné Michel Bertignac Fabian Blanchard Abdoul Ahad Cissé Catherine Dichmont Sophie Gourguet Olivier Guyader Pierre‐Yves Hardy Sarah Jennings Lorne Richard Little Claire Macher David Jonathan Mills Ahmed Noussair Sean Pascoe Jean‐Christophe Pereau Nicolas Sanz Anne‐Maree Schwarz Tony Smith Olivier Thébaud 《Fish and Fisheries》2017,18(6):1056-1072
Reconciling food security, economic development and biodiversity conservation is a key challenge, especially in the face of the demographic transition characterizing many countries in the world. Fisheries and marine ecosystems constitute a difficult application of this bio‐economic challenge. Many experts and scientists advocate an ecosystem approach to manage marine socio‐ecosystems for their sustainability and resilience. However, the ways by which to operationalize ecosystem‐based fisheries management (EBFM) remain poorly specified. We propose a specific methodological framework—viability modelling—to do so. We show how viability modelling can be applied using four contrasted case‐studies: two small‐scale fisheries in South America and Pacific and two larger‐scale fisheries in Europe and Australia. The four fisheries are analysed using the same modelling framework, structured around a set of common methods, indicators and scenarios. The calibrated models are dynamic, multispecies and multifleet and account for various sources of uncertainty. A multicriteria evaluation is used to assess the scenarios’ outcomes over a long time horizon with different constraints based on ecological, social and economic reference points. Results show to what extent the bio‐economic and ecosystem risks associated with the adoption of status quo strategies are relatively high and challenge the implementation of EBFM. In contrast, strategies called ecoviability or co‐viability strategies, that aim at satisfying the viability constraints, reduce significantly these ecological and economic risks and promote EBFM. The gains associated with those ecoviability strategies, however, decrease with the intensity of regulations imposed on these fisheries. 相似文献