939 resultados para PHRAGMITES-AUSTRALIS


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The non-native, invasive genotype of the common reed ( Phragmites australis (Cav.) Trin. ex Steudel) has become a problem of significant proportions throughout wetlands of North America (Saltonstall 2001). Although attempts to suppress or eradicate Phragmites have utilized a wide variety of techniques, herbicides have generally been most effective (Marks et al. 1994). In the spring, mid-summer, and late summer of 2003, we attempted to opportunistically control Phragmites in five freshwater ponds within Cape Cod National Seashore (CCNS) by repeatedly severing stems underwater, at ground level.(PDF has 4 pages.)

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Les plantes envahissantes sont considérées comme l'une des plus grandes menaces sur les espèces, mais leurs impacts sur les amphibiens demeurent peu connus. L’objectif de ce projet est de déterminer l’effet de l’établissement du roseau commun (Phragmites australis) sur la répartition des amphibiens et sur leur développement larvaire. Il est présumé que cette plante s'accapare l'espace et les ressources disponibles en produisant une importante biomasse, qu’elle peut modifier l’hydrologie des marais et la structure des communautés d’amphibiens. J’ai évalué les facteurs influençant la répartition des amphibiens selon les caractéristiques des étangs et du paysage dans 50 sites envahis ou non à divers degrés. Des expériences ont également été menées afin d’étudier les répercussions de trois densités de roseau sur des têtards de la Grenouille des bois (Lithobates sylvaticus) et sur la qualité de son habitat. Mes résultats suggèrent que le roseau à forte densité ralentit le développement larvaire de la grenouille des bois et influence les assemblages phytoplanctoniques. Cependant, il n’y a aucune relation entre la densité de la plante et la survie, la morphologie des têtards et les caractéristiques biotiques et abiotiques de l’eau. Dans notre aire d’étude, le paysage autour des étangs a une plus grande influence sur la répartition des amphibiens que l'établissement du roseau. Toutefois, la probabilité d’assèchement est plus élevée lorsque la plante est établie en grande quantité, ce qui, si l’envahissement s’intensifie, aura un effet néfaste sur la survie des têtards et mettra en péril la persistance des populations.

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Mémoire numérisé par la Division de la gestion de documents et des archives de l'Université de Montréal

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Invasive plant species threaten natural areas by reducing biodiversity and altering ecosystem functions. They also impact agriculture by reducing crop and livestock productivity. Millions of dollars are spent on invasive species control each year, and traditionally, herbicides are used to manage invasive species. Herbicides have human and environmental health risks associated with them; therefore, it is essential that land managers and stakeholders attempt to reduce these risks by utilizing the principles of integrated weed management. Integrated weed management is a practice that incorporates a variety of measures and focuses on the ecology of the invasive plant to manage it. Roadways are high risk areas that have high incidence of invasive species. Roadways act as conduits for invasive species spread and are ideal harborages for population growth; therefore, roadways should be a primary target for invasive species control. There are four stages in the invasion process which an invasive species must overcome: transport, establishment, spread, and impact. The aim of this dissertation was to focus on these four stages and examine the mechanisms underlying the progression from one stage to the next, while also developing integrated weed management strategies. The target species were Phragmites australis, common reed, and Cisrium arvense, Canada thistle. The transport and establishment risks of P. australis can be reduced by removing rhizome fragments from soil when roadside maintenance is performed. The establishment and spread of C. arvense can be reduced by planting particular resistant species, e.g. Heterotheca villosa, especially those that can reduce light transmittance to the soil. Finally, the spread and impact of C. arvense can be mitigated on roadsides through the use of the herbicide aminopyralid. The risks associated with herbicide drift produced by application equipment can be reduced by using the Wet-Blade herbicide application system.

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O atenolol é um fármaco β-bloqueador normalmente encontrado em águas residuais devido à incapacidade que os processos convencionais de tratamento destas águas têm em removê-lo. Neste trabalho foram utilizados microcosmos de leitos construídos de macrófitas de fluxo sub-superficial utilizando uma matriz de argila expandida (LECA) e plantados com Phragmites australis para avaliar a sua capacidade em remover atenolol das águas residuais. Para a detecção e quantificação do atenolol em soluções aquosas (águas e efluentes) desenvolveu-se e optimizou-se uma metodologia analítica usando separação cromatográfica por HPLC e detecção espectrofotométrica por diode array (HPLC-DAD) ou por ultravioleta visível (HPLC-UV-Vis). Desenvolveu-se também um procedimento de limpeza e concentração de amostra por extracção em fase sólida (SPE), o qual foi utilizado sempre que as concentrações do analito se encontraram abaixo dos limites de quantificação do equipamento. A utilização desta metodologia de HPLC, combinada com uma eficaz pré-concentração por SPE, resultou num método analítico com um limite de quantificação muito reduzido (9 ngmL-1) e elevada reprodutibilidade (RSD<4%). A eficiência de remoção de atenolol pelos sistemas de macrófitas estudados foi de 93% após um tempo de retenção de 4 dias. Foram testados leitos só com LECA e com LECA e plantas para remoção do atenolol. Nos leitos só com LECA, a cinética de remoção foi caracterizada por um rápido passo inicial (uma remoção de aproximadamente 75% após apenas 24 h), o qual é frequentemente atribuído à adsorção na matriz de LECA. A remoção de atenolol nos leitos de LECA continuou a aumentar de forma constante até ao final do ensaio (8 dias), sendo, contudo cerca de 5-10% mais baixo do que o valor observado nos leitos das plantas após os 4 primeiros dias. Para o tempo de retenção de 4 dias a maioria do atenolol é removido pela matriz de LECA, porém um acréscimo de cerca de 12-14% relativamente à eficiência de remoção global pode ser atribuído às plantas (Phragmites australis), o que está de acordo com trabalhos anteriormente publicados. Apesar de ser necessário realizar mais testes utilizando sistemas em larga escala, de modo a conseguir avaliar totalmente o comportamento do atenolol num sistema de leitos construídos de macrófitas, o presente estudo apresenta a possibilidade de aplicar este tipo de sistemas, relativamente baratos, no tratamento de águas residuais contaminadas com atenolol. ABSTRACT: Atenolol is a β-blocker drug commonly found in wastewaters due to the inability of the conventional wastewater treatment processes to remove it. ln this study, subsurface flow constructed wetland microscosm systems have been established with a matrix of light expanded clay aggregates (LECA) and planted with Phragmites australis in order to evaluate their ability to remove atenolol from wastewater. For the detection and quantification of atenolol in aqueous solutions (water and wastewater), an adequate analytical methodology was developed and optimized using chromatographic separation by HPLC and diode array (DAD) or UV-Vis spectrophotometric detection. A sample clean-up and preconcentration procedure by solid phase extraction (SPE) was also developed for use whenever the concentration levels of the analyte were below the instrument's limit of quantification. Combined with an efficient SPE concentration step, the use of HPLC yielded an analytical method for atenolol quantification with very low LOQ (9 ngmL-1) and high reproducibility (RSD< 4%). Overall atenolol removal efficiency of 93% was achieved after a retention time of only 4 days with the microcosm systems planted with Phragmites australis. The removal kinetics was characterized by an initial fast step (removal of about 75% after just 24h) which is mainly attributable to adsorption on the LECA matrix. Atenolol removal in LECA beds continues to increase in a steady pace up to the end of the assay (8 days) being nevertheless about 5-l 0% lower than those observed in the planted beds after the first 4 days. For the retention time of 4 days most of the atenolol is removed by the LECA matrix but an additional 12-14% to the overall removal efficiency can be attributed to the Phragmites plants, which comes in agreement with other published reports. Despite the fact that further tests using larger­ scale systems are required to fully evaluate the atenolol behavior in a constructed wetland system, this study points out to the possible application of these low-cost wastewater systems to treat atenolol contaminated wastewater.

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Novel species of fungi described in the present study include the following from South Africa: Alanphillipsia aloeicola from Aloe sp., Arxiella dolichandrae from Dolichandra unguiscati, Ganoderma austroafricanum from Jacaranda mimosifolia, Phacidiella podocarpi and Phaeosphaeria podocarpi from Podocarpus latifolius, Phyllosticta mimusopisicola from Mimusops zeyheri and Sphaerulina pelargonii from Pelargonium sp. Furthermore, Barssia maroccana is described from Cedrus atlantica (Morocco), Codinaea pini from Pinus patula (Uganda), Crucellisporiopsis marquesiae from Marquesia acuminata (Zambia), Dinemasporium ipomoeae from Ipomoea pes-caprae (Vietnam), Diaporthe phragmitis from Phragmites australis (China), Marasmius vladimirii from leaf litter (India), Melanconium hedericola from Hedera helix (Spain), Pluteus albotomentosus and Pluteus extremiorientalis from a mixed forest (Russia), Rachicladosporium eucalypti from Eucalyptus globulus (Ethiopia), Sistotrema epiphyllum from dead leaves of Fagus sylvatica in a forest (The Netherlands), Stagonospora chrysopyla from Scirpus microcarpus (USA) and Trichomerium dioscoreae from Dioscorea sp. (Japan). Novel species from Australia include: Corynespora endiandrae from Endiandra introrsa, Gonatophragmium triuniae from Triunia youngiana, Penicillium coccotrypicola from Archontophoenix cunninghamiana and Phytophthora moyootj from soil. Novelties from Iran include Neocamarosporium chichastianum from soil and Seimatosporium pistaciae from Pistacia vera, Xenosonderhenia eucalypti and Zasmidium eucalyptigenum are newly described from Eucalyptus urophylla in Indonesia. Diaporthe acaciarum and Roussoella acacia are newly described from Acacia tortilis in Tanzania. New species from Italy include Comoclathris spartii from Spartium junceum and Phoma tamaricicola from Tamarix gallica. Novel genera include (Ascomycetes): Acremoniopsis from forest soil and Collarina from water sediments (Spain), Phellinocrescentia from a Phellinus sp. (French Guiana), Neobambusicola from Strelitzia nicolai (South Africa), Neocladophialophora from Quercus robur (Germany), Neophysalospora from Cotymbia henryi (Mozambique) and Xenophaeosphaeria from Grewia sp. (Tanzania). Morphological and culture characteristics along with ITS DNA barcodes are provided for all taxa.

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Novel species of fungi described in the present study include the following from South Africa: Alanphillipsia aloeicola from Aloe sp., Arxiella dolichandrae from Dolichandra unguiscati, Ganoderma austroafricanum from Jacaranda mimosifolia, Phacidiella podocarpi and Phaeosphaeria podocarpi from Podocarpus latifolius, Phyllosticta mimusopisicola from Mimusops zeyheri and Sphaerulina pelargonii from Pelargonium sp. Furthermore, Barssia maroccana is described from Cedrus atlantica (Morocco), Codinaea pini from Pinus patula (Uganda), Crucellisporiopsis marquesiae from Marquesia acuminata (Zambia), Dinemasporium ipomoeae from Ipomoea pes-caprae (Vietnam), Diaporthe phragmitis from Phragmites australis (China), Marasmius vladimirii from leaf litter (India), Melanconium hedericola from Hedera helix (Spain), Pluteus albotomentosus and Pluteus extremiorientalis from a mixed forest (Russia), Rachicladosporium eucalypti from Eucalyptus globulus (Ethiopia), Sistotrema epiphyllum from dead leaves of Fagus sylvatica in a forest (The Netherlands), Stagonospora chrysopyla from Scirpus microcarpus (USA) and Trichomerium dioscoreae from Dioscorea sp. (Japan). Novel species from Australia include: Corynespora endiandrae from Endiandra introrsa, Gonatophragmium triuniae from Triunia youngiana, Penicillium coccotrypicola from Archontophoenix cunninghamiana and Phytophthora moyootj from soil. Novelties from Iran include Neocamarosporium chichastianum from soil and Seimatosporium pistaciae from Pistacia vera, Xenosonderhenia eucalypti and Zasmidium eucalyptigenum are newly described from Eucalyptus urophylla in Indonesia. Diaporthe acaciarum and Roussoella acacia are newly described from Acacia tortilis in Tanzania. New species from Italy include Comoclathris spartii from Spartium junceum and Phoma tamaricicola from Tamarix gallica. Novel genera include (Ascomycetes): Acremoniopsis from forest soil and Collarina from water sediments (Spain), Phellinocrescentia from a Phellinus sp. (French Guiana), Neobambusicola from Strelitzia nicolai (South Africa), Neocladophialophora from Quercus robur (Germany), Neophysalospora from Cotymbia henryi (Mozambique) and Xenophaeosphaeria from Grewia sp. (Tanzania). Morphological and culture characteristics along with ITS DNA barcodes are provided for all taxa.

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Habitat requirements of fish are most strict during the early life stages, and the quality and quantity of reproduction habitats lays the basis for fish production. A considerable number of fish species in the northern Baltic Sea reproduce in the shallow coastal areas, which are also the most heavily exploited parts of the brackish marine area. However, the coastal fish reproduction habitats in the northern Baltic Sea are poorly known. The studies presented in this thesis focused on the influence of environmental conditions on the distribution of coastal reproduction habitats of freshwater fish. They were conducted in vegetated littoral zone along an exposure and salinity gradient extending from the innermost bays to the outer archipelago on the south-western and southern coasts of Finland, in the northern Baltic Sea. Special emphasis was placed on reed-covered Phragmites australis shores, which form a dominant vegetation type in several coastal archipelago areas. The main aims of this research were to (1) develop and test new survey and mapping methods, (2) investigate the environmental requirements that govern the reproduction of freshwater fish in the coastal area and (3) survey, map and model the distribution of the reproduction habitats of pike (Esox lucius) and roach (Rutilus rutilus). The white plate and scoop method with a standardized sampling time and effort was demonstrated to be a functional method for sampling the early life stages of fish in dense vegetation and shallow water. Reed-covered shores were shown to form especially important reproduction habitats for several freshwater fish species, such as pike, roach, other cyprinids and burbot, in the northern Baltic Sea. The reproduction habitats of pike were limited to sheltered reed- and moss-covered shores of the inner and middle archipelago, where suitable zooplankton prey were available and the influence of the open sea was low. The reproduction habitats of roach were even more limited and roach reproduction was successful only in the very sheltered reed-covered shores of the innermost bay areas, where salinity remained low (< 4‰) during the spawning season due to freshwater inflow. After identifying the critical factors restricting the reproduction of pike and roach, the spatial distribution of their reproduction habitats was successfully mapped and modelled along the environmental gradients using only a few environmental predictor variables. Reproduction habitat maps are a valuable tool promoting the sustainable use and management of exploited coastal areas and helping to maintain the sustainability of fish populations. However, the large environmental gradients and the extensiveness of the archipelago zone in the northern Baltic Sea demand an especially high spatial resolution of the coastal predictor variables. Therefore, the current lack of accurate large-scale, high-resolution spatial data gathered at exactly the right time is a considerable limitation for predictive modelling of shallow coastal waters.

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古民族植物学(Paleoethnobotany)在我国尚属一个比较年轻的学科,其主要研究对象是先民们所栽培或利用过的植物遗存(Plant remains),目的在于揭示古代人们对食物的选择,栽培植物的起源,早期农业的出现以及居址周围的自然与生态环境。吐鲁番地区降水稀少。干燥的环境,使得考古遗址中的植物遗存得以完好的保存。本论文首次对吐鲁番洋海墓地(2500 B. P. )的包括木材、果实、种子、茎杆、叶片等在内的植物遗存进行了系统的研究,依此分析了当时的植被及环境,并对与当时的土著居民密切相关的植物类群进行了详细研究。 研究表明,吐鲁番洋海墓地植物群包括木材、禾本科粮食作物、杂草及其它植物共18 种。其中我们详细研究了14 种,隶属于7 科14 属,它们分别为禾本科黍属中的黍(Panicum miliaceum),大麦属中的青稞(Hordeum vulgare var. nudum),小麦属中的普通小麦(Triticum aestivum),芦苇属的芦苇(Phragmites australis),虎尾草属的虎尾草(Chloris virgata),小獐毛属的小獐毛(Aeluropus pungens var. pungens),稗属的稗子(Echinochloa crusgali),大麻科大麻属中的大麻(Cannabis sativa),紫草科紫草属中的小花紫草(Lithospermum officinale), 豆科槐属中的苦豆子(Sophora alopecuroides var. alopecuroides),茄科枸杞属中的黑果枸杞(Lycium ruthenicum),松科云杉属中的云杉属未定种(Picea sp.), 杨柳科杨属的胡杨(Popules euphratica)及柳属未定种(Salix sp.)。研究表明,这些植物遗存渗透到古洋海人生活的方方面面。其中,粮食作物为可能以黍为主,以普通小麦及青稞为辅;用以作装饰的为小花紫草的小坚果;可能与其原始宗教及医药相关的为大麻;与建筑相关的植物有芦苇、黑果枸杞、云杉(Picea sp.)、胡杨及柳(Salix sp.)等;与当地居民意义不大的杂草有稗子、苦豆子、小獐毛、虎尾草等。其中,大麻及小花紫草遗存的出土意味着当时的土著居民对当地的植物已经有了很高的认识水平;黍、青稞及普通小麦的出土意味着他们可能与东西方文化均有接触,为东西方文明的交融起了桥梁作用;所出土的部份植物如小獐毛、小花紫草、柳、苦豆子,尤其是稗子、芦苇及香蒲属植物等都属于喜湿植物。这说明,在当时的洋海墓地周边环境与今天相似,亦为一块植被丰富的绿洲,其中可能有大面积的湿地。

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生物入侵在全世界广泛发生,目前已经受到全球关注。入侵生物对群落生物多样性和生态系统功能造成严重威胁,导致严重的环境问题和惨重的经济损失。薇甘菊(Mikania micrantha)、五爪金龙(Ipomoea cairica)和南美蟛蜞菊(Wedelia trilobata)是我国华南地区危害最严重的三种外来入侵种,其中以薇甘菊危害最严重,是世界十大有害杂草之一。从20世纪80年代发生以来,薇甘菊已在我国广东农林区域造成严重危害。 机械防治、化学防治和传统的生物防治等治理措施,未能有效治理外来入侵种的危害,直到使用本地种菟丝子(Cuscuta spp)的防治策略。与从原产地引进有害生物天敌的传统生物防治方法不同,本地种由于适应当地气候且与其他物种协同进化,因此,对生态环境潜在的负作用小。从2000年,被发现寄生和抑制薇甘菊之后,菟丝子被认为是防治薇甘菊的有效措施。 为了探讨菟丝子寄生对外来入侵种的治理,及对入侵群落的恢复,本研究在内伶仃岛的林地(入侵种群落被引入菟丝子寄生1-4年),以及东莞、深圳和海丰的干扰样地(入侵种群落被菟丝子自然寄生5年以上)开展野外调查。在每个样地分别设立外来种入侵亚群和菟丝子治理亚群,通过测定群落结构与组成、土壤性质与养分含量,以及外来种和菟丝子的生长与养分含量等参数之后,本研究得出以下主要结论。 (1) 虽然,被寄生的外来入侵种薇甘菊、五爪金龙和南美蟛蜞菊通过调节资源分配以抵御南方菟丝子(Cuscuta australis)的寄生影响,但是,菟丝子寄生导致外来入侵种生物量降低、繁殖能力下降、养分含量降低。虽然,很多寄生植物都是广谱寄生,能同时寄生多种寄主植物,但是,在本研究的被入侵的群落中,菟丝子主要寄生外来入侵植物。尤其是寄生于南美蟛蜞菊和薇甘菊的菟丝子,生长旺盛、繁殖能力强,表现出高度的适应性。因此,菟丝子对外来入侵种(南美蟛蜞菊和薇甘菊)有寄生偏好性,并对本地种的负面影响小。 (2) 通过吸收寄主的养分,田野菟丝子(Cuscuta campestris)有效地抑制了薇甘菊的危害。由于入侵种的凋落物养分含量高且分解效率高,而且,菟丝子能够促进其它凋落物的分解,并使难以被植物吸收的养分转化成易于被吸收利用的状态。因此,菟丝子与薇甘菊的寄生作用导致土壤养分含量的升高。在薇甘菊被抑制之后,本地种利用丰富的土壤养分资源,提高生长适应性,增强抵抗入侵的能力,甚至抵制薇甘菊的再生。 (3) 菟丝子的寄生作用改变了外来寄主与本地非寄主的竞争平衡,促进本地植物的生长与重建。在外来种被抑制之后,本地种的丰度和群落的物种多样性逐渐增加。本地种如:野葛(Pueraria lobata)和芦苇(Phragmites australis),取代了入侵群落中的入侵种,成了群落的优势种。而其它原先被薇甘菊抑制的本地草本、藤本和灌木,在引入菟丝子防治之后长势较好。群落稳定性与物种多样性密切相关,被治理群落本地种的增加有利于群落的演替与稳定。 (4) 被干扰的生态系统往往更容易被外来种入侵,而外来入侵种又常导致人工干扰生境的严重退化。在人工干扰样地的菟丝子对薇甘菊的抑制效果与在林地的效果一致,导致被寄生的薇甘菊生长衰退、养分竞争能力下降、入侵危害能力降低。而在薇甘菊被菟丝子治理之后,土壤养分资源增加,入侵群落的物种丰度和生物多样性提高。本 地种的重建与本地群落的恢复密切相关,利于本地被治理群落的稳定,促进被干扰植被的恢复。 菟丝子是一种治理外来入侵种危害的有效措施,适用于破碎的生境和被干扰的生态系统,尤其是在采用目前防治措施难以治理的情况下。本研究为本地种防治外来入侵种提供科学依据,且表明以入侵地的本地种治理外来入侵种有可能成为有效且可持续发展的生物防治策略。