984 resultados para invasive plant
Resumo:
There has been recent interest in determining the upper limits to the feasibility of weed eradication. Although a number of disparate factors determine the success of an eradication program, ultimately eradication feasibility must be viewed in the context of the amount of investment that can be made. The latter should reflect the hazard posed by an invasion, with greater investment justified by greater threats. In simplest terms, the effort (and hence investment) to achieve weed eradication comprises the detection effort required to delimit an invasion plus the search and control effort required to prevent reproduction until extirpation occurs over the entire infested area. The difficulty of estimating the required investment at the commencement of a weed eradication program (as well as during periodic reviews) is a serious problem. Bioeconomics show promise in determining the optimal approach to managing weed invasions, notwithstanding ongoing difficulties in estimating the costs and benefits of eradication and alternative invasion management strategies. A flexible approach to the management of weed invasions is needed, allowing for the adoption of another strategy when it becomes clear that the probability of eradication is low, owing to resourcing or intractable technical issues. Whether the considerable progress that has been achieved towards eradication of the once massive witchweed invasion can be duplicated for other weeds of agricultural systems will depend to a large extent upon investment (. $250 million over 50 yr in this instance). Weeds of natural ecosystems seem destined to remain more difficult eradication targets for a variety of reasons, including higher impedance to eradication, more difficulty in valuing the benefits arising from eradication, and possibly less willingness to pay from society at large.
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Aim: Birds play a major role in the dispersal of seeds of many fleshy-fruited invasive plants. The fruits that birds choose to consume are influenced by fruit traits. However, little is known of how the traits of invasive plant fruits contribute to invasiveness or to their use by frugivores. We aim to gain a greater understanding of these relationships to improve invasive plant management. Location: South-east Queensland, Australia. Methods: We measure a variety of fruit morphology, pulp nutrient and phenology traits of a suite of bird-dispersed alien plants. Frugivore richness of these aliens was derived from the literature. Using regressions and multivariate methods, we investigate relationships between fruit traits, frugivore richness and invasiveness. Results: Plant invasiveness was negatively correlated to fruit size, and all highly invasive species had quite similar fruit morphology [smaller fruits, seeds of intermediate size and few (<10) seeds per fruit]. Lower pulp water was the only pulp nutrient trait associated with invasiveness. There were strong positive relationships between the diversity of bird frugivores and plant invasiveness, and in the diversity of bird frugivores in the study region and another part of the plants' alien range. Main conclusions: Our results suggest that weed risk assessments (WRA) and predictions of invasive success for bird-dispersed plants can be improved. Scoring criteria for WRA regarding fruit size would need to be system-specific, depending on the fruit-processing capabilities of local frugivores. Frugivore richness could be quantified in the plant's natural range, its invasive range elsewhere, or predictions made based on functionally similar fruits.
Resumo:
Hendersonia osteospermi was found for the first time in Australia on leaf spots of the introduced invasive plant Chrysanthemoides monilifera ssp. rotundata (bitou bush) in coastal regions of New South Wales. Pathogenicity tests on species from 11 tribes in the family Asteraceae, demonstrated that H. osteospermi caused severe necrosis on leaves and stems of C. monilifera ssp. rotundata and its congener C. monilifera ssp. monilifera (boneseed). Small necrotic spots also developed on Osteospermum fruticosum and Dimorphotheca cuneata in the Calenduleae and on Helianthus annuus (sunflower) in the Heliantheae. None of the other plant species tested developed leaf spots, although H. osteospermi was re-isolated from senescent leaves of Cynara scolymus (globe artichoke) in the Cynareae and Vernonia cinerea in the Vernonieae. Single ascospores from ascomata of a Pleospora-like fungus found on diseased stems of bitou bush produced H. osteospermi in culture, which proved the anamorph/teleomorph connection. The ITS region of both a single-ascospore isolate and a single-conidium isolate were sequenced and found to be identical. The taxonomic status of H. osteospermi is re-examined and Austropleospora osteospermi gen. et sp. nov. is described as its teleomorph based on morphology, host range tests and DNA sequence analysis. The potential of A. osteospermi for the biological control of bitou bush and boneseed in Australia is discussed.
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The genus Asparagus includes at least six invasive species in Australia. Asparagus aethiopicus and A. africanus are invasive in subtropical Australia, and a third species, A. virgatus is naturalized and demonstrates localized spread in south east Queensland. To better understand how the attributes of these species contribute to their invasiveness, we compared fruit and seed traits, germination, seedling emergence, seed survival, and time-to-maturity. We further investigated dispersal ecology of A. africanus, examining the diet of a local frugivore, the figbird (Sphecotheres viridis) and the effect of gut passage on seedling emergence. Overall, A. aethiopicus was superior in germination and emergence, with the highest mean germination (98.8%) and emergence (94.5%) under optimal conditions and higher emergence (mean of 73.3%) across all treatments. In contrast, A. africanus had the lowest germination under optimal conditions (71.7%) and low mean seedling emergence (49.5%), but had fruits with the highest relative yield (ratio of dry pulp to fruit fresh weight) that were favored by a local frugivore. Figbirds consumed large numbers of A. africanus fruits (~30% of all non-Ficus fruits), and seedling germination was not significantly affected by gut passage compared to unprocessed fruits. Asparagus virgatus germinated poorly under cool, light conditions (1.4%) despite a high optimum mean (95.0%) and had low mean performance across emergence treatments (36.3%). The species also had fruits with a low pulp return for frugivores. For all species, seed survival declined rapidly in the first 12 mo and fell to < 3.2% viability at 36 mo. On the basis of the traits considered, A. virgatus is unlikely to have the invasive potential of its congeners. Uniformly short seed survival times suggest that weed managers do not have to contend with a substantial persistent soil-stored seed bank, but frugivore-mediated dispersal beyond existing infestations will present a considerable management challenge.
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Of the 70 cases of classical biological control for the protection of nature found in our review, there were fewer projects against insect targets (21) than against invasive plants (49), in part, because many insect biological control projects were carried out against agricultural pests, while nearly all projects against plants targeted invasive plants in natural ecosystems. Of 21 insect projects, 81% (17) provided benefits to protection of biodiversity, while 48% (10) protected products harvested from natural systems, and 5% (1) preserved ecosystem services, with many projects contributing to more than one goal. In contrast, of the 49 projects against invasive plants, 98% (48) provided benefits to protection of biodiversity, while 47% (23) protected products, and 25% (12) preserved ecosystem services, again with many projects contributing to several goals. We classified projects into complete control (pest generally no longer important), partial control (control in some areas but not others), and "in progress," for projects in development for which outcomes do not yet exist. For insects, of the 21 projects discussed, 59% (13) achieved complete control of the target pest, 18% (4) provided partial control, and 41% (9) are still in progress. By comparison, of the 49 invasive plant projects considered, 27% (13) achieved complete control, while 33% (16) provided partial control, and 47% (24) are still in progress. For both categories of pests, some projects' success ratings were scored twice when results varied by region. We found approximately twice as many projects directed against invasive plants than insects and that protection of biodiversity was the most frequent benefit of both insect and plant projects. Ecosystem service protection was provided in the fewest cases by either insect or plant biological control agents, but was more likely to be provided by projects directed against invasive plants, likely because of the strong effects plants exert on landscapes. Rates of complete success appeared to be higher for insect than plant targets (59% vs 27%), perhaps because most often herbivores gradually weaken, rather than outright kill, their hosts, which is not the case for natural enemies directed against pest insects. For both insect and plant biological control, nearly half of all projects reviewed were listed as currently in progress, suggesting that the use of biological control for the protection of wildlands is currently very active.
Resumo:
Navua sedge, a member of the Cyperaceae family, is an aggressive weed of pastures in Fiji, Sri Lanka, Malay Peninsula, Vanuatu, Samoa, Solomons, and Tahiti and is now a weed of pastures and roadsides in north Queensland, Australia. Primarily restricted to areas with an annual rainfall exceeding 2500 mm, Navua sedge is capable of forming dense stands smothering many tropical pasture species. Seventeen herbicides were field tested at three sites in north Queensland, with glyphosate, halosulfuron, hexazinone, imazapic, imazapyr, or MSMA the most effective for Navua sedge control. Environmental problems such as persistence in soil, lack of selectivity and movement off-site may occur using some herbicides at the predicted LC90 control level rates. A seasonality trial using halosulfuron (97.5 g ai/ha) gave better Navua sedge control (84%) spraying March to September than spraying at other times (50%). In a frequency trial, sequential glyphosate applications (2,160 g ae/ha) every two months was more effective for continued Navua sedge control (67%) than a single application of glyphosate (36%), though loss of ground cover would occur. In a management trial, single applications of glyphosate (2,160 to 3,570 g ae/ha) using either a rope wick, ground foliar spraying or a rotary rope wick gave 59 to 73% control, while other treatments (rotary hoe (3%), slashing (-13%) or crushing (-30%)) were less effective. In a second management trial, four monthly rotary wick applications were much more effective (98%) than four monthly crushing applications (42%). An effective management plan must include the application of regular herbicide treatments to eliminate Navua sedge seed being added to the soil seed bank. Treatments that result in seed burial, for example, discing are likely to prolong seed persistence and should be avoided. The sprouting activity of vegetative propagules and root fragmentation needs to also be considered when selecting control options.
Resumo:
The feasibility of state-wide eradication of 41 invasive plant taxa currently listed as ‘Class 1 declared pests’ under the Queensland Land Protection (Pest and Stock Route Management) Act 2002 was assessed using the predictive model ‘WeedSearch’. Results indicated that all but one species (Alternanthera philoxeroides) could be eradicated, provided sufficient funding and labour were available. Slightly less than one quarter (24.4%) (n = 10) of Class 1 weed taxa could be eradicated for less than $100 000 per taxon. An additional 43.9% (n = 18) could be eradicated for between $100 000 and $1M per taxon. Hence, 68.3% of Class 1 weed taxa (n = 28) could be eradicated for less than $1M per taxon. Eradication of 29.3% (n = 12) is predicted to cost more than $1M per taxon. Comparison of these WeedSearch outputs with either empirical analysis or results from a previous application of the model suggests that these costs may, in fact, be underestimates. Considering the likelihood that each weed will cost the state many millions of dollars in long-term losses (e.g. losses to primary production, environmental impacts and control costs), eradication seems a wise investment. Even where predicted costs are over $1M, eradication can still offer highly favourable benefit:cost ratios. The total (cumulative) cost of eradication of all 41 weed taxa is substantial; for all taxa, the estimated cost of eradication in the first year alone is $8 618 000. This study provides important information for policy makers, who must decide where to invest public funding.
Resumo:
Macfadyena unguis-cati (L.) Gentry (Bignoniaceae) is a major environmental weed in coastal Queensland, Australia. There is a lack of quantitative data on its leaf chemistry and its impact on soil properties. Soils from infested vs uninfested areas, and leaves of M. unguis-cati and three co-occurring vine species (one exotic, two native) were collected at six sites (riparian and non-riparian) in south-eastern Queensland. Effects of invasion status, species, site and habitat type were examined using univariate and multivariate analyses. Habitat type had a greater effect on soil nutrients than on leaf chemistry. Invasion effect of M. unguis-cati on soil chemistry was more pronounced in non-riparian than in riparian habitat. Significantly higher values were obtained in M. unguis-cati infested (vs. uninfested) soils for ~50% of traits. Leaf ion concentrations differed significantly between exotic and native vines. Observed higher leaf-nutrient load (especially nitrogen, phosphorus and potassium) in exotic plants aligns with the preference of invasive plant species for disturbed habitats with higher nutrient input. Higher load of trace elements (aluminium, boron, cadmium and iron) in its leaves suggests that cycling of heavy-metal ions, many of which are potentially toxic at excess level, could be accelerated in soils of M. unguis-cati-invaded landscape. Although inferences from the present study are based on correlative data, the consistency of the patterns across many sites suggests that M. unguis-cati may improve soil fertility and influence nutrient cycling, perhaps through legacy effects of its own litter input.
Resumo:
Chromolaena odorata (L.) King and Robinson (Siam weed) is a highly invasive plant and a high priority for control in north Queensland. It can be effectively treated using high-volume, groundbased herbicide spray equipment, but operational information shows that this control method becomes increasingly difficult in areas where vehicle access is prevented by rougher terrain. Low-volume, high-concentration herbicide applications have proven capable of causing high mortality in these remote situations. Two trials were undertaken between May 2010 and May 2012 to refine effective rates of aminopyralid/fluroxypyr, fluroxypyr and metsulfuron-methyl, only using low-volume, high-concentration applications on Siam weed. Fluroxypyr on its own was as effective as aminopyralid/fluroxypyr as both herbicides caused 95-100% mortality at overlapping rates containing 5 to 18.85 g a.i. L-1 of fluroxypyr. Metsulfuron-methyl caused 100% mortality when applied at 3 and 6 g a.i. L-1. Effective control was achieved with approximately 16 to 22 mL of the solutions per plant, so a 5 L mixture in a backpack could treat 170 to 310 adult plants. There are several options for treating Siam weed on the ground and the choice of methods reflects the area, plant density and accessibility of the infestation. Control information from Siam weed field crews shows that low volume, high concentration herbicide applications applied using a splatter gun are a more efficient method for controlling larger, denser remote infestations than physical removal. By identifying effective herbicides that are applied through low-volume equipment, these trials provide an additional and more efficient tool for controlling Siam weed in remote areas.
Resumo:
Suomenlinna on yksi Helsingin suosituimmista matkailu- ja kulttuurinähtävyyksistä. Kustaanmiekan, samoin kuin koko Suomenlinnan luonto on muodostunut perinteisestä suomalaisesta saaristoluonnosta ja vuosisatojen saatossa paikalle tulleista linnoituksien kasvistosta. Saaren vaihtelevien elinympäristöjen johdosta alueen kasvillisuus on hyvin rikasta. Linnoituksien monet kasvilajit ovat tulleet tulokaskasveina eri puolilta Eurooppaa sekä Venäjältä. Suurin osa Suomenlinnan alueesta on kallioketoa ja tämän lisäksi myös valliketoa, joista molemmat kuuluvat suojeltaviin alueisiin. Kustaanmiekan niityillä kasvaa keto- ja paahdelajeja, kuten harvinaista ketonoidanlukkoa (Botrychium lunaria L.) sekä ketoneilikkaa (Dianthus deltoides L.). Tämän tutkimuksen ensisijaisena tarkoituksena oli kartoittaa Kustaanmiekan alueen kesäkauden 2009 ketokasvilajisto ja eri putkilokasvilajien runsaus. Tutkimuksessa selvitettiin myös maaperätekijöiden ja alueen hoitohistorian mahdollista vaikutusta ketokasvilajistoon. Tutkimuksessa kartoitettiin kymmenen eri kedon kasvillisuus Suomenlinnan Kustaanmiekan linnoitusalueella. Kedot sijaitsivat eri puolilla Kustaanmiekkaa, sellaisilla paikoilla, missä ketokasvillisuus oli runsainta. Maastotyöt suoritettiin kesä- ja heinäkuussa laskemalla jokaisen kedon ruutujen putkilokasvien peittävyydet sekä listaamalla ylös myös ruutujen ulkopuoliset kevät- ja loppukesän kukkijat touko- ja elokuussa. Maaperän ominaisuuksien määrittämiseksi otettiin kultakin kedolta pintamaanäytteet elokuussa. Muita tutkittuja muuttujia olivat maapinnan kaltevuus sekä sammalen, karikkeen, paljaan maan, kenttäkasvillisuuden pohjakerros ja kallion osuus tutkimusruuduilla. Ketojen kasvillisuuden keskimääräinen korkeus mitattiin kesä- ja heinäkuussa. Kasvistossa oli selviä eroavaisuuksia ketojen välillä. Kasvilajien määrä vaihteli ketojen kokonaislajimäärän ollessa 40-60 kasvilajia. Yhteensä kedoilta löytyi 120 eri putkilokasvilajia, joista useimmat kukkivat sekä kesä- että heinäkuussa. Ketojen kasvilajimäärä vaihteli yhdellä neliömetrillä 6,3-13,6 kasvilajiin, minkä lisäksi Shannon-Wienerin diversiteetti-indeksi vaihteli 1,4-2,3 arvon välillä. Yleisimpiä lajeja, joita kedoilla tavattiin, olivat muun muassa siankärsämö (Achillea millefolium L.), koiranheinä (Dactylis glomerata L.), juolavehnä (Elymus repens L.) ja hopeahanhikki (Potentilla argentea L.). Alueella kasvoi myös muutamia sotatulokaslajeja kuten harmiota (Berteroa incana L.), ukonpalkoa (Bunias orientalis L.) ja karvahorsmaa (Epilobium hirsutum L.). Maaperätekijöillä, kuten suurella fosforin pitoisuudella ei ollut vaikutusta kasvilajien määrään kedoilla. Vain maan pH ja johtoluku korreloivat positiivisesti ketojen kasvillisuuden korkeuden kanssa. Vaikka tulosten perusteella ketojen hoidolla ei ollut vaikutusta ketojen kasvillisuuden määrään, voidaan kuitenkin olettaa oikeanlaisen hoidon parantavan tyypillisten ketokasvien kilpailukykyä muita niittykasveja kohtaan.
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O processo de introdução de espécies é reconhecido como a segunda causa mais importante de erosão da diversidade biológica em muitos ambientes no Brasil e no mundo. As espécies invasoras possuem não apenas o poder de sobrevivência e adaptação em outros ambientes, mas a capacidade de dominar a diversidade biológica nativa através da alteração das características básicas dos processos ecológicos naturais e das interações. A jaqueira, Artocarpus heterophyllus Lamarck (Moraceae), tem sua origem nas florestas tropicais da Índia, tendo sido introduzida no Brasil ainda no período Colonial e atualmente é invasora em áreas de Mata Atlântica. Este estudo fornece os primeiros dados sobre a influência da espécie exótica invasora Artocarpus heterophyllus sobre comunidades de anuros de folhiço. As amostragens foram realizadas em uma área de Mata Atlântica, no litoral sudoeste do estado do Rio de Janeiro, incluindo informações sobre riqueza de espécies, densidades específicas e parâmetros ambientais. Nosso estudo foi realizado no Parque Estadual da Ilha Grande entre janeiro de 2009 e março de 2011. Para amostrar a comunidade de anuros de folhiço usamos 154 parcelas de 5 x 5 m, sendo 77 delas em áreas com jaqueiras e 77 em áreas sem jaqueiras, totalizando 3.850 m de chão de floresta amostrados. Nós amostramos um total de 613 anuros habitando o chão da floresta, pertencentes a dez espécies: Brachycephalus didactylus; Chiasmocleis sp.; Haddadus binotatus; Ischnocnema guentheri; Ischnocnema octavioi; Ischnocnema parva; Leptodactylus marmoratus; Physalaemus signifer; Rhinnela ornata e Zachaenus parvulus. Seis das dez espécies foram comuns às áreas com e sem jaqueiras, sendo a similaridade entre as duas áreas de 60%. As áreas com jaqueiras tiveram o dobro (N = 18) de parcelas sem nenhum anfíbio. O número de anfíbios registrados nas parcelas com jaqueiras (38%) foi menor do que o encontrado nas áreas sem jaqueiras (62%). O anfíbio predominante no folhiço em ambas às condições foi Ischnocnema parva, tendo abundancia maior nas parcelas sem jaqueiras. A densidade total de anuros vivendo no chão da floresta nas áreas com jaqueiras (12,2 ind/100 m) foi menor que nas áreas sem jaqueiras (19,7 ind/100 m). Entre os parâmetros ambientais analisados os que possuíram maior influência sobre a abundância de anfíbios foram a profundidade do folhiço e o pH do solo. Os dados sugerem que a jaqueira, além de ocupar o habitat de espécies nativas, é capaz de promover alterações na estrutura desses habitats que irão intervir na fauna do local.
Resumo:
生物入侵作为全球变化的一部分,已经引起广泛的关注;而群落可入侵性是生物入侵研究的核心和热点问题之一。本文以原产墨西哥,广泛入侵我国西南地区的紫茎泽兰(Eupatorium adenophorum)为例:首先,对西南地区被紫茎泽兰入侵的群落和生境进行了分类;然后,就地形、本地植物物种多样性、环境梯度等对群落可入侵性的影响进行了探讨;最后,对紫茎泽兰的空间分布格局进行了模拟和预测。 在小尺度上,紫茎泽兰入侵与本地植物物种多样性呈负相关,表明资源的可利用性可能是调节群落可入侵性的主导因素;本地植物物种多样性在群落演替过程中和入侵的早期抑制紫茎泽兰入侵;在大的尺度上,物理环境的变异超过了内在生物因子的重要性,本地植物物种多样性与紫茎泽兰入侵成功呈正相关。 紫茎泽兰主要通过公路和河流在我国西南地区入侵和扩散;资源的可利用性是影响公路和河流两侧群落可入侵性的关键因子。 紫茎泽兰分布中心主要在沧源、元江和西昌;位于分布区边缘的乐业、重庆和泸定有可能成为新的分布中心,并对邻近地区,尤其北面和东面的区域形成繁殖体压力;紫茎泽兰整体上有向东和向北扩散的趋势。目前主要分布在云贵高原,将来的分布区还将以云贵高原为核心。
Resumo:
紫茎泽兰(Eupatorium adenophorum Spreng.)种子萌发的温度范围是10-30 ℃,最适宜的萌发温度是25℃,高温显著抑制其萌发,35 ℃恒温即没有种子萌发。紫茎泽兰种子萌发对于光的需求为中等,在黑暗中发芽率为17%。紫茎泽兰种子萌发的pH 范围是5.0-7.0,最高发芽率是以蒸馏水为介质,其pH为5.7。紫茎泽兰种子的萌发率随着水势的加大而逐渐降低,在水势大于-0.7 MPa 条件下,即没有种子萌发。在盐分含量小于100 mM NaCl 条件下,其发芽率均大于65%;在盐分含量小于250 mM条件下,其发芽率仍大于10%,当盐分含量达到300 mM NaCl时,即没有种子萌发。紫茎泽兰种子在土壤表层其发芽率最高,当埋藏深度为1.5 cm时即没有种子萌发。根据我们所得的实验结果,对比其原产地的气候条件并结合我国的气候条件和土壤条件进行分析,我们预测紫茎泽兰未来在中国的分布范围将局限在云贵高原,尽管在某些气候和土壤环境适宜的条件下仍有可能会形成零星分布区。 研究了紫茎泽兰和飞机草(Eupatorium odoratum L.)在三种环境胁迫条件下(高温、低温、干旱)七种抗氧化酶活性的变化。结果表明:这三种环境胁迫都对两种植物的生物膜系统造成了损伤,造成了植物体内丙二醛含量的升高。紫茎泽兰在这三种环境胁迫条件下,DHAR活性都升高;SOD活性也都升高,但是在低温处理时与对照的差别并不明显;POD和GR活性在低温和干旱处理时升高,在高温处理时降低;CAT活性在高温和干旱处理时降低,在低温处理时升高;MDAR活性在在高温和干旱处理时降低,在低温处理时略微上升,但是与对照的差别并不明显;APX活性则在三种环境胁迫下表现各不相同。通过这些结果可以说明:DHAR对紫茎泽兰抵抗不良环境的损伤具有重要作用。 而飞机草的抗氧化酶系统的变化为:SOD、APX和DHAR在三种环境胁迫下酶活性都升高;CAT在高温胁迫下升高,而在低温和干旱胁迫下酶活性降低;POD和MDAR在高温和干旱胁迫下酶活性升高,而在低温胁迫下酶活性降低;GR在高温和干旱胁迫下酶活性升高,而在低温胁迫下保持不变。以上的研究结果说明,SOD、APX和DHAR是飞机草抵御环境胁迫的关键酶。 通过比较两种植物在温度胁迫下抗氧化酶系统的不同响应,我们研究发现:两种植物之所以对温度的忍耐性不同,在一定程度上是由于它们在温度胁迫时抗氧化酶系统所作出的不同响应,抗氧化酶系统很可能在两种植物抵抗温度胁迫过程中扮演重要角色,即通过有效调节抗氧化酶活性来减少植物体内有害物质-活性氧自由基的积累,从而减少对植物细胞膜的损伤。两者的差别主要是:紫茎泽兰在低温胁迫时,清除活性氧的抗氧化酶都增加,这就减轻了活性氧自由基在植物细胞中的积累,从而可以在一定程度上保护植物。但是,在高温胁迫时CAT, POD, APX, GR和MDAR酶活性并没有随着SOD活性的升高而升高,所以很有可能造成对细胞有毒害作用的H2O2累积,其结果就造成了紫茎泽兰在高温胁迫下叶片细胞膜的过氧化程度较强。而飞机草的情况正相反,在低温胁迫下飞机草叶片细胞膜的过氧化程度较强,抗氧化酶的协调上升出现在飞机草遭受高温胁迫时,而当其处于低温胁迫时抗氧化酶间的变化趋势则出现了很大分歧,这说明飞机草在高温胁迫时较低温胁迫时能够较好地保护自身遭受活性氧自由基的伤害。
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紫茎泽兰(Eupatorium adenophorum Spreng.)作为重要的外来入侵种之一,已严重破坏了入侵地生态系统的结构与功能,同时使当地农林业生产蒙受巨大的损失。因此,明确紫茎泽兰的竞争策略与扩散潜力,对制定合理的控制措施具有重要意义。 土壤氮素增加常常有助于外来种的入侵,那么降氮能否抵制入侵呢?向土壤中添加碳素,增强微生物对氮素的吸收,从而降低土壤中可被植物吸收的氮素是目前常用的降氮方法。为检验这一假说对入侵种紫茎泽兰的适用性,选取入侵种紫茎泽兰和本地种禾本科雀麦(Bromus japonicus)、菊科鱼眼草(Dichrocephala integrifolia),分别单栽或与紫茎泽兰混栽,向各植物组合中添加碳素(按1650克有机质/平方米计)或氮素(按30克氮素/平方米计),并设立对照进行盆栽实验。在碳素添加条件下,紫茎泽兰地上与地下生物量分别比对照降低了71.9% 和 74.9%,而本地种的生物量却没有受到显著影响。同时,碳素添加导致紫茎泽兰对本地种的竞争强度(RII)明显下降。氮素添加则减弱或逆转了上述碳素的作用。因此,向土壤中添加碳素有助于抵抗氮沉降对外来种入侵的促进作用,特别对抵御那些与氮素有亲和力的入侵种更为有效。在不同氮素条件下,紫茎泽兰对本地种竞争中,资源竞争强度均明显大于化感作用。尽管在紫茎泽兰发育早期化感作用较小,但是,碳素添加使紫茎泽兰可利用氮素减少,激发了化感作用在竞争中占有更大的比例,说明资源竞争与化感是相互结合、共同发挥作用的。 去叶作为模拟采食方法之一,至少可以通过两种方式影响植物竞争。一是去叶对目标种生长产生负面影响,二是邻种去叶有利于目标种生长,进而改变种间竞争关系。基于以上假定,对紫茎泽兰与相邻本地种分别单栽、同种合栽和异种混栽,进行去叶处理。结果恰与假定相悖:在整个生长季内,去叶增加目标株生物量的1.0 – 198.9%。对于入侵种而言,当邻居本地种去叶时,紫茎泽兰能完全弥补竞争产生的负面效应,即它与未去叶的单栽紫茎泽兰生长无显著差异;而紫茎泽兰去叶降低了相邻本地种的生长,加剧了原本由于竞争给对本地种带来的负面影响。因此,去叶效应与邻种的存在与否及邻种的类型均有关。在应用生物控制对目标株采食时,特别是在没有造成严重伤害或致死情况下,可以使本来具有竞争优势的入侵种变得更具强势。竞争与去叶之间存在复杂的相互作用,采食带来的间接效应可能比预想的更为复杂。因此,在生物控制措施实施之前,充分地估计生物控制的间接作用至关重要。 为检验反应—扩散模型(reaction–diffusion model)能否正确模拟紫茎泽兰小尺度扩散速率,本研究调查了四川攀枝花山区5个不同的生境的紫茎泽兰群落。对各样地内紫茎泽兰定位和年龄确定,基于克里金插值法做出其入侵格局的等年线图,通过等年线之间的垂直距离即可得到紫茎泽兰扩散速率的经验值。同时,计算内禀增长率和扩散系数,根据模型计算得到扩散速率的预测值。结果表明:紫茎泽兰扩散速率经验值明显小于模型预测值。因此,尽管反应—扩散模型已在大尺度扩散预测方面得到广泛的应用和验证,但在小尺度上,由于没有借助于复杂的生活史模型和分层模型,单凭反应—扩散模型不足以得到准确的预测。另外,在没有遭受干扰的生境中,可以发现紫茎泽兰扩散早期存在明显的时滞期。倘若这种时滞效应在入侵扩散中是频繁发生的,那么在判定物种是否具有入侵性时,很可能由于物种处于时滞期而被误认为非入侵种。 基于紫茎泽兰入侵至中国60年来所收集到的441已知分布记录和23个环境变量,采用GARP模型对其潜在分布范围做出了预测,并通过Kappa和ROC(receiver–operator characteristic)对预测结果进行检验。结果表明紫茎泽兰目前分布以云贵高原为主体,逐渐向四川盆地东部、山东半岛、东南沿海、台湾沿海以及海南岛等地扩散。冷季降水量、年极端低温和年均最高温对分布影响较大。RDA(Redundancy Analysis)分析结果显示温度和降水是限制紫茎泽兰扩散的重要因素。在过去的20年里,紫茎泽兰已经从温度较高、天气波动较小的亚热带气候逐渐向气候温凉、降水减少的高海拔地区扩散。紫茎泽兰可以适应相对较宽的温度和降水梯度,年均温度在10—22 ˚C,年降水量在800—2000 mm区间均有分布。本研究结果为发展早期预警工作、防止紫茎泽兰在中国进一步入侵提供了科学依据。
Resumo:
Cotoneaster pannosus (Rosaceae), an ornamental shrub native to China, is reported for the first time in Tarragona Province (Catalonia, Spain). Data on demography and accompanying species for the new locality are provided, in addition to a chrorological update at nation level.