18 resultados para Mesquite


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Quilpie mesquite (Prosopis velutina) is an invasive woody weed that is believed to have been introduced into south-west Queensland in the 1930s. Following the withdrawal of 2,4,5-T, research on P. pallida resulted in revised recommendations for control of all Prosopis spp. in Queensland. Adoption of many of these recommendations for Quilpie mesquite control produced substandard results. Following a pilot trial, a shade-house experiment was conducted to determine the differences in susceptibility of two species of mesquite, P. velutina and P. pallida, to commonly available herbicides. It was hypothesized that P. velutina was less susceptible than P. pallida, based upon claims that the registered chemical recommendations for Prosopis spp. were not sufficiently effective on P. velutina. Nine foliar herbicide treatments were applied to potted shade-house plants. Treatment effects indicated differing susceptibility between the two species. P. velutina consistently showed less response to metsulfuron, fluroxypyr, 2,4-D/picloram and triclopyr/picloram, compared to the glyphosate formulations, where negligible differences occurred between the two species. The response to glyphosate was poor at all rates in this experiment. Re-application of herbicides to surviving plants indicated that susceptibility can decrease when follow-up application is in autumn and the time since initial application is short. The relationship between leaf structure and the volume of spray adhering to a plant was assessed across species. The herbicide captured by similar-sized plants of each species differed, with P. pallida retaining a greater volume of herbicide.

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Literature cited: p. 181-185.

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Issued Oct. 1977.

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Designing practical rules for controlling invasive species is a challenging task for managers, particularly when species are long-lived, have complex life cycles and high dispersal capacities. Previous findings derived from plant matrix population analyses suggest that effective control of long-lived invaders may be achieved by focusing on killing adult plants. However, the cost-effectiveness of managing different life stages has not been evaluated. We illustrate the benefits of integrating matrix population models with decision theory to undertake this evaluation, using empirical data from the largest infestation of mesquite (Leguminosae: Prosopis spp) within Australia. We include in our model the mesquite life cycle, different dispersal rates and control actions that target individuals at different life stages with varying costs, depending on the intensity of control effort. We then use stochastic dynamic programming to derive cost-effective control strategies that minimize the cost of controlling the core infestation locally below a density threshold and the future cost of control arising from infestation of adjacent areas via seed dispersal. Through sensitivity analysis, we show that four robust management rules guide the allocation of resources between mesquite life stages for this infestation: (i) When there is no seed dispersal, no action is required until density of adults exceeds the control threshold and then only control of adults is needed; (ii) when there is seed dispersal, control strategy is dependent on knowledge of the density of adults and large juveniles (LJ) and broad categories of dispersal rates only; (iii) if density of adults is higher than density of LJ, controlling adults is most cost-effective; (iv) alternatively, if density of LJ is equal or higher than density of adults, management efforts should be spread between adults, large and to a lesser extent small juveniles, but never saplings. Synthesis and applications.In this study, we show that simple rules can be found for managing invasive plants with complex life cycles and high dispersal rates when population models are combined with decision theory. In the case of our mesquite population, focussing effort on controlling adults is not always the most cost-effective way to meet our management objective.

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This project is led by scientists in conservation decision appraisal and brings together a group of experts working across the Lake Eyre Basin (LEB). The LEB covers a sixth of Australia, with an array of globally significant natural values that are threatened by invasive plants, among other things. Managers at various levels are investing in attempts to control, contain and eradicate these invasive plant species, under severe time and resources limitations. To date there has been no basin-wide assessment of which weed management strategies and locations provide the best investments for maximising outcomes for biodiversity per unit cost. Further, there has been no assessment of the extent of ecosystem intactness that may be lost without effective invasive plant species management strategies. Given that there are insufficient resources to manage all invasive plant species everywhere, this information has the potential to improve current investment decisions. Here, we provide a prioritisation of invasive plant management strategies in the LEB. Prioritisation was based on cost-effectiveness for biodiversity benefits. We identify the key invasive plant species to target to protect ecosystem intactness across the bioregions of the LEB, the level of investment required and the likely reduction in invasive species dominance gained per dollar spent on each strategy. Our focus is on strategies that are technically and socially feasible and reduce the likelihood that high impact invasive plant species will dominate native ecosystems, and therefore change their form and function. The outputs of this work are designed to help guide decision-making and further planning and investment in weed management for the Basin. Experts in weed management, policy-making, community engagement, biodiversity and natural values of the Basin, attended a workshop and agreed upon 12 strategies to manage invasive plants. The strategies focused primarily on 10 weeds which were considered to have a high potential for broad, significant impacts on natural ecosystems in the next 50 years and for which feasible management strategies could be defined. Each strategy consisted of one or more supporting actions, many of which were spatially linked to IBRA (Interim Biogeographical Regionalisation of Australia) bioregions. The first strategy was an over-arching recommendation for improved mapping, information sharing, education and extension efforts in order to facilitate the more specific weed management strategies. The 10 more specific weed management strategies targeted the control and/or eradication of the following high-impact exotic plants: mesquite, parkinsonia, rubber vine, bellyache bush, cacti, mother of millions, chinee apple, athel pine and prickly acacia, as well as a separate strategy for eradicating all invasive plants from one key threatened ecological community, the GAB (Great Artesian Basin dependant) mound springs. Experts estimated the expected biodiversity benefit of each strategy as the reduction in area that an invasive plant species is likely to dominate in over a 50-year period, where dominance was defined as more than 30% coverage at a site. Costs were estimated in present day terms over 50 years largely during follow up discussions post workshop. Cost-effectiveness was then calculated for each strategy in each bioregion by dividing the average expected benefit by the average annual costs. Overall, the total cost of managing 12 invasive plant strategies over the next 50 years was estimated at $1.7 billion. It was estimated that implementation of these strategies would result in a reduction of invasive plant dominance by 17 million ha (a potential 32% reduction), roughly 14% of the LEB. If only targeting Weeds of National Significance (WONS), the total cost was estimated to be $113 million over the next 50 years. Over the next 50 years, $2.3 million was estimated to eradicate all invasive plant species from the Great Artesian Basin Mound Springs threatened ecological community. Prevention and awareness programs were another key strategy targeted across the Basin and estimated at $17.5 million in total over 50 years. The cost of controlling, eradicating and containing buffel grass were the most expensive, over $1.5 billion over 50 years; this strategy was estimated to result in a reduction in buffel grass dominance of a million ha in areas where this species is identified as an environmental problem. Buffel grass has been deliberately planted across the Basin for pasture production and is by far the most widely distributed exotic species. Its management is contentious, having economic value to many graziers while posing serious threats to biodiversity and sites of high cultural and conservation interest. The strategy for containing and locally eradicating buffel grass was a challenge to cost based on expert knowledge, possibly because of the dual nature of this species as a valued pastoral grass and environmental weed. Based on our conversations with experts, it appears that control and eradication programs for this species, in conservation areas, are growing rapidly and that information on the most cost-effective strategies for this species will continue to develop over time. The top five most cost-effective strategies for the entire LEB were for the management of: 1) parkinsonia, 2) chinee apple, 3) mesquite, 4) rubber vine and 5) bellyache bush. Chinee apple and mother of millions are not WONS and have comparatively small populations within the semi-arid bioregions of Queensland. Experts felt that there was an opportunity to eradicate these species before they had the chance to develop into high-impact species within the LEB. Prickly acacia was estimated to have one of the highest benefits, but the costs of this strategy were high, therefore it was ranked 7th overall. The buffel grass strategy was ranked the lowest (10th) in terms of cost effectiveness. The top five most cost-effective strategies within and across the bioregions were the management of: 1) parkinsonia in the Channel Country, 2) parkinsonia in the Desert Uplands, 3) mesquite in the Mitchell Grass Downs, 4) parkinsonia in the Mitchell Grass Downs, and 5) mother of millions in the Desert Uplands. Although actions for several invasive plant species like parkinsonia and prickly acacia were concentrated in the Queensland part of the LEB, the actions involved investing in containment zones to prevent the spread of these species into other states. In the NT and SA bioregions of the LEB, the management of athel pine, parkinsonia and cacti were the main strategies. While outside the scientific research goals of study, this work highlighted a number of important incidental findings that led us to make the following recommendations for future research and implementation of weed management in the Basin: • Ongoing stakeholder engagement, extension and participation is required to ensure this prioritisation effort has a positive impact in affecting on-ground decision making and planning. • Short term funding for weed management was identified as a major reason for failure of current efforts, hence future funding needs to be secure and ongoing. • Improved mapping and information sharing is essential to implement effective weed management. • Due to uncertainties in the outcomes and impacts of management options, strategies should be implemented as part of an adaptive management program. The information provided in this report can be used to guide investment for controlling high-impact invasive plant species for the benefits of biodiversity conservation. We do not present a final prioritisation of invasive plant strategies for the LEB, and we have not addressed the cultural, socio-economic or spatial components necessary for an implementation plan. Cost-effectiveness depends on the objectives used; in our case we used the intactness of ecosystems as a surrogate for expected biodiversity benefits, measured by the extent that each invasive plant species is likely to dominate in a bioregion. When other relevant factors for implementation are considered the priorities may change and some actions may not be appropriate in some locations. We present the costs, ecological benefits and cost-effectiveness of preventing, containing, reducing and eradicating the dominance of high impact invasive plants through realistic management actions over the next 50 years. In doing so, we are able to estimate the size of the weed management problem in the LEB and provide expert-based estimates of the likely outcomes and benefits of implementing weed management strategies. The priorities resulting from this work provide a prospectus for guiding further investment in management and in improving information availability.

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The issue of the usefulness of different prosopis species versus their status as weeds is a matter of hot debate around the world. The tree Prosopis juliflora had until 2000 been proclaimed weedy in its native range in South America and elsewhere in the dry tropics. P. juliflora or mesquite has a 90-year history in Sudan. During the early 1990s a popular opinion in central Sudan and the Sudanese Government had begun to consider prosopis a noxious weed and a problematic tree species due to its aggressive ability to invade farmlands and pastures, especially in and around irrigated agricultural lands. As a consequence prosopis was officially declared an invasive alien species also in Sudan, and in 1995 a presidential decree for its eradication was issued. Using a total economic valuation (TEV) approach, this study analysed the impacts of prosopis on the local livelihoods in two contrasting irrigated agricultural schemes. Primarily a problem-based approach was used in which the derivation of non-market values was captured using ecological economic tools. In the New Halfa Irrigation Scheme in Kassala State, four separate household surveys were conducted due to diversity between the respective population groups. The main aim was here to study the magnitude of environmental economic benefits and costs derived from the invasion of prosopis in a large agricultural irrigation scheme on clay soil. Another study site, the Gandato Irrigation Scheme in River Nile State represented impacts from prosopis that an irrigation scheme was confronted with on sandy soil in the arid and semi-arid ecozones along the main River Nile. The two cases showed distinctly different effects of prosopis but both indicated the benefits to exceed the costs. The valuation on clay soil in New Halfa identified a benefit/cost ratio of 2.1, while this indicator equalled 46 on the sandy soils of Gandato. The valuation results were site-specific and based on local market prices. The most important beneficial impacts of prosopis on local livelihoods were derived from free-grazing forage for livestock, environmental conservation of the native vegetation, wood and non-wood forest products, as well as shelterbelt effects. The main social costs from prosopis were derived from weeding and clearing it from farm lands and from canalsides, from thorn injuries to humans and livestock, as well as from repair expenses vehicle tyre punctures. Of the population groups, the tenants faced most of the detrimental impacts, while the landless population groups (originating from western and eastern Sudan) as well as the nomads were highly dependent on this tree resource. For the Gandato site the monetized benefit-cost ratio of 46 still excluded several additional beneficial impacts of prosopis in the area that were difficult to quantify and monetize credibly. In River Nile State the beneficial impact could thus be seen as completely outweighing the costs of prosopis. The results can contributed to the formulation of national and local forest and agricultural policies related to prosopis in Sudan and also be used in other countries faced with similar impacts caused by this tree.

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O dimorfismo sexual exibido por machos polifênicos em algumas espécies do gênero Ptychoderes envolve variação no rostro, antena e ventritos. A existência de polifenismo pode ser um importante componente no processo evolutivo por meio de novidades morfológicas e comportamentais. O objetivo desse estudo foi determinar a variação em caracteres morfométricos, polifenismo em machos, variação de estruturas com conhecido dimorfismo sexual, possíveis padrões alométricos e testar estas inferências para Ptychoderes através do mapeamento do dimorfismo sexual e de machos em uma reconstrução filogenética de Ptychoderes usando Mesquite 2.04. Foram medidas 23 variáveis morfométricas em 510 espécimes com as seguintes análises realizadas: análises de cluster, analises de componentes principais (PCA), analise de variáveis canônicas (AVC), análise de regressão por eixo maior reduzido (RMA). Cada tipo de dimorfismo foi mapeado em uma filogenia prévia como dois estados separados usando parcimônia. Para todas as espécies o dimorfismo sexual apresentou diferenças significativas entre os sexos com relação aos segmentos antenais (II- X).O compriemtno do rosto e ventrito V foram confirmados como indicativos de dimorfismo sexual (exceto em P. jordani). A única espécie em que não ocorreu machos polifenicos foi P. depressus. Nas outras espécies machos grandes e pequenos diferem significantemente para muitas variáveis com similaridades e diferenças. Na ACP, o primeiro componente (PC1) apresentou alta porcentagem de variância nos dados de todas as espécies; apresentou loadings de mesmo sinal sugerindo diferenças relacionadas ao tamanho para as espécies P. jordani, P. depressus, P. virgatus, P. mixtus e P. callosus e para as espécies P. viridanus, P. antiquus, P. elongates e P. nebulosus apresentou loadings positivos e negativos sugerindo diferenças relacionadas a forma (alometria). O PC2 apresentou loadings positivos e negativos para todas as espécies, um provável componente alométricos. A AVC confirmou os grupos: machos grandes, machos pequenos e fêmeas quando estes ocorreram. Nós encontramos diferentes padrões alométricos para todas as espécies com diferenças e semelhanças entre as espécies. Todos esses resultados confirmam a hipótese de polifenismo em machos e dimorfismo sexual para Ptychhoderes. A análise dos padrões alométricos para o dimorfismo sexual revelou alometria positiva para o comprimento do rostro (CR1) em machos e fêmeas, com os ventritos apenas em machos. Padrões alométricos positivos relacionados ao polifenismo nos antenômeros foram confirmados para os machos grandes e pequenos de quase todas as espécies exceto em P. nebulosus. O ancestral de clados na filogenia de Ptychoderes foi inferido para machos polifênicos (exceto P. depressus) com variáveis no rostro, antenas e ventritos indicativas de dimorfismo sexual com alometria positiva. Estes padrões poderiam estar ligados com o comportamento de proteção das fêemeas realizados por machos grandes durante a oviposição.

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囊瓣芹属Pternopetalum Franchet是伞形科Apiaceae/Umbelliferae芹亚科Apioideae芹族Apieae重要成员。全属包括约32个分类群(包括变种),分布于南朝鲜、日本、中国的西南部和邻近的喜马拉雅地区,中国西南部的横断山区是其多样性中心。典型的东亚特有格局和对东亚亚热带森林环境的偏爱是其东亚区系故有份子的特征。 基于19个标本馆标本材料、野外调查以及相应的实验证据,本博士论文从三个研究主题对囊瓣芹属展开了全面而系统的研究。一是通过标本观察和野外调查,利用标本管理系统BRAHMS和表型分析软件包DELTA系统,完成了囊瓣芹属的世界性分类修订;二是基于上述的分类方案,选择伞形科其它属的44个种作为参考性类群(Reference taxa),利用Winclada, NONA和MESQUITE软件包开展了分支系统学研究;三是基于坐标化的点分布数据,利用DIVA-GIS系统的生态位模型,进行潜在分布预测和生态地理分布特征的分析。研究的主要初步结论如下: 一、分类修订 根据对19个标本馆标本材料(包括85个模式采集)的考证,以及对云南、四川、贵州等地野外居群的观察,结合DELTA系统的表型分析,本研究确认囊瓣芹属包含14个种,提出了14个新异名,属下分为东亚囊瓣芹组Sect. I. Pteridophyllae H. Wolff和囊瓣芹组Sect. II. Pternopetalum H. Wolff两个组的分类方案。前者包括东亚囊瓣芹P. tanakae (Sav. & Franchet) Hand.-Mazz.、高山囊瓣芹P. subalpinum Hand.-Mazz.、洱源囊瓣芹P. molle (Franchet) Hand.-Mazz.等5个种;后者包括五匹青P. vulgare (Dunn) Hand.-Mazz.、囊瓣芹P. davidii Franchet和澜沧囊瓣芹P. delavayi (Franchet) Hand.-Mazz.等9个种。萼齿、花柱基、和花柱的形态是区别两个组比较好的形态学特征。叶的着生位置、最终末回裂片的形状(是否异形)、分裂回数以及伞形花序着生的位置和果棱表面的附属构造是种间识别有用的检索特征。 二、系统发育分析 根据如上的14个种的分类方案,另外选取了伞形科小芹属Sinocarum H. Wolff、丝瓣芹属Acronema Falc. ex Edgew.和鸭儿芹属Cryptotaenia L.等10个属共44种作为参考类群,基于63个广义形态学性状和58个种的形态学矩阵,利用最大简约法对囊瓣芹属进行了分支分析。结果表明,囊瓣芹属的14个种与日本特有单型的仙洞草Chamaele decumbens (Thunb.)Makino.形成一个单独分支,处于分支图的基部位置。表明囊瓣芹属与鸭儿芹属有较近的亲缘关系。长枝吸引可能是造成Chamaele Miq.与东亚囊瓣芹分支的非正常聚合的原因。囊瓣芹属可能是单系内群,但它与Chamaele Miq.属间关系需要进一步研究。属下形成以五匹青P. vulgare和东亚囊瓣芹P. tanakae为代表的两个主干演化线。分支进化(Cladogenesis)在两个主干演化线形成了形态和地理上对称分布的“种对”。根据形态特征的变异和地理分布,这些“种对”分为三种类型:1、形态上多变而地理上广布的类型,以东亚囊瓣芹P. tanakae和五匹青P. vulgare为代表;2、形态上稳定地理上狭域特有的类型,以薄叶囊瓣芹P. leptophyllum (Dunn)Hand.-Mazz. 和川鄂囊瓣芹P. rosthornii (Diels) Hand.-Mazz.为代表;3、形态上趋同而多变,地理分布上几乎完全重叠的类型,以洱源囊瓣芹P. molle和澜沧囊瓣芹P. delavayi为代表。 性状状态的分析显示,属下形态特征的趋异具有较强的同朔性。不等长的伞辐和花梗,以及囊状的花瓣基部三个形态学特征可以标识包括仙洞草在内的囊瓣芹分支。祖征状态的重建表明,东亚囊瓣芹分支相对保留了更多的祖征,是属下相对原始的类型;五匹青分支是后期生境需求的特化,适应潮湿和荫蔽环境的衍生类型。 三、生态地理分布 基于1128个坐标化的点分布数据和生态位模型,利用地理信息系统软件包DIVA-GIS对囊瓣芹属的物种多样性、现代地理分布、潜在分布进行了分析。结果表明,二郎山-峨眉山地区以及重庆金佛山及其临近地区是囊瓣芹属的两个主要的多样性中心。分布区内局部尺度上的异常性多样性(Diversity abnormalies)可能有两个来源:一是高的异质性生境条件下物种形成速率的差异;二是中国西南山地的“冰原岛峰效应”(Nunataks),比如峨眉山和金佛山,对属的早期演化线成员所起到的“避难所”(Refuge)的作用。 所预测的潜在分布范围与观察到的地理分布范围是一致的,说明对特化的气候忍耐性是限制囊瓣芹属物种地理分布的主要因素。温度和降水的季节性变化对囊瓣芹属代表中的地理分布限制作用比较大。亚热带-高山针阔常绿林是属下物种比较适宜的生境。属的地理分布可能形成于中新世以后,生态位的保守性是解释囊瓣芹属东亚本土就地分化和多样化的原因。属的分布范围的形成可能经历了一个早期南退西进的过程,后期分布范围变化可能主要是东西方向上的迁移和扩展。喜马拉雅—横断山—峨眉山/金佛山/神农架—日本、南朝鲜一线是囊瓣芹属多样化过程中分布范围东西延伸的重要通道。喜马拉雅—中国西南—日本朝鲜亚热带森林植被的完整性和连续性是囊瓣芹属演化和分布区形成的基本条件。

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The order Scorpiones is one of the most cytogenetically interesting groups within Arachnida by virtue of the combination of chromosome singularities found in the 59 species analyzed so far. In this work, mitotic and meiotic chromosomes of 2 species of the family Bothriuridae were detailed. This family occupies a basal position within the superfamily Scorpionoidea. Furthermore, review of the cytogenetic data of all previously studied scorpions is presented. Light microscopy chromosome analysis showed that Bothriurus araguayae and Bothriurus rochensis possess low diploid numbers compared with those of species belonging to closely related families. Gonadal cells examined under light and in transmission electron microscopy revealed, for the first time, that the Bothriuridae species possess typical monocentric chromosomes, and male meiosis presented chromosomes with synaptic and achiasmatic behavior. Moreover, in the sample of B. araguayae studied, heterozygous translocations were verified. The use of techniques to highlight specific chromosomal regions also revealed additional differences between the 2 Bothriurus species. The results herein recorded and the overview elaborated using the available cytogenetic information of Scorpiones elucidated current understanding regarding the processes of chromosome evolution that have occurred in Bothriuridae and in Scorpiones as a whole.

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Based on climate data and occurrence records, ecological niche models (ENM) are an important opportunity to identify areas at risk or vulnerable to biological invasion. These models are based on the assumption that there is a match between the climatic characteristic of native and invaded regions predicting the potential distribution of exotic species. Using new methods to measure niche overlap, we chose two exotic species fairly common in semi-arid regions of South America, Prosopis juliflora (Sw.) D.C. and Prosopis pallida (H. ; B. ex. Willd) HBK, to test the climate matching hypothesis. Our results indicate that both species occur with little niche overlap in the native region while the inverse pattern is observed in the invaded region on South America, where both species occur with high climatic overlap. Maybe some non-climate factor act limiting the spread of P. pallida on the native range. We believe that a founder effect can explain these similarities between species niche in the invaded region once the seeds planted in Brazil came from a small region on the Native range (Piura in Peru), where both species occur sympatric. Our hypothesis of a founder effect may be evident when we look at the differences between the predictions of the models built in the native and invaded ranges. Furthermore, our results indicate that P. juliflora shows high levels of climate matching between native and invaded ranges. However, conclusions about climate matching of P. pallida should be taken with caution. Our models based on climatic variables provide multiple locations suitable for occurrence of both species in regions where they still don t have occurrence records, including places of high interest for conservation.

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The ground pods of mesquite (GPM) was submitted to different thermal treatments for two hours after wanted temperature stabilization, for making of the treatments: A = ground pods of mesquite without heat treatment (approximately 30 degrees C); B = The ground pods of mesquite treated at 60 degrees C; C = The ground pods of mesquite treated at 80 degrees C; D = The ground pods of mesquite treated at 100 degrees C and E = The ground pods of mesquite treated at 120 degrees C. Soon after, samples were collected for accomplishment for chemical analyses and in vitro digestibility. A completely randomized design with three replications was utilized. The DM, CP, NFE, CF, ADF, celluloses, lignin, ash and CE values, did not were affected (P>0.05) by temperature. It was observed a quadratic effect (P<0.01) on the contents of EE, decreasing linear effect (P<0.01) on the CC and increasing linear effect on the NDF (P<0.01) and Hemicellulose (P<0.05) contents. The in vitro dry matter digestibility and the in vitro organic matter digestibility were not affected (P>0.05) by temperature. on the other hand the in vitro protein digestibility level, showed a quadratic effect (P<0.05), decreasing after 54 degrees C.

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This research was carried out to evaluate the ruminal degradation of dry matter (DM), crude protein (CP) and neutral detergent fiber (NDF) of silages of elephant grass (Pennisetum purpureum) cutting in 70; 90 and 110 days after regrowth with inclusion of 0; 5; 10 and 15% of mesquite (Prosopis juliflora) meal, based on natural matter in a completely randomized design, in split plot arrangement. Samples of silages were incubated in the rumen of two Jersey cows for 3; 6; 12; 24; 48; 72 and 96 h, and the bags at time "zero" were only washed with water to determine the soluble fraction. There was not interaction (P> 0.05) incubation time x inclusion of mesquite pods x cutting age of the grass for DM degradability, there was only interaction (P <0.05) between these factors for CP and NDF degradability. The most effective DM degradability (42.54%) was observed for 15% inclusion of mesquite pods. The effective CP degradability was higher (69.04%) for elephant grass silage with 70 days after regrowth with 15% of mesquite pods. The inclusion of mesquite pods in elephant grass silages improve DM, CP and NDF degradability, while increment of the age after regrowth result in reduction of this parameters.