938 resultados para Honey plants
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"Some publications consulted" : p.[8]
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Mode of access: Internet.
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本论文从传粉生物学的角度出发,运用野外观察、室内测定和生物统计学方法,对毛乌素沙地的两种蜜源植物羊柴(Hedysarum leave)和角蒿(Incarvillea sinensis var. sinensis)的开花物候、花生物学特性、传粉昆虫行为以及繁育系统进行了研究,得出如下结论: 1.在自然居群中,存在着开白色花和紫红色花的两种羊柴植株,其中白色花植株仅占5.5±1.56%左右。白色花和紫红色花植株的花期存在明显的重叠,白色花植株的花期集中在8月中旬到9月上旬,而紫红色花植株的花期从7月中旬持续到9月中旬。在整个花期内,单个白色花植株的生产的总花数为125±11.33朵,明显少于紫红色花植株的372±30.38朵,两者存在极显著差异。 2. 羊柴白色花和紫红色花的单花花粉量、胚珠数和P/O值都存在显著差异。在单花开放的整个过程中,白色花的花蜜分泌量显著地高于紫红色花,但白色花和紫红色花的花蜜糖分浓度变化趋势相似,即都具有两个花蜜浓度高峰值。 3. 羊柴白色花植株稳定且访花频率较高的传粉者是散熊蜂、白脸条蜂和意大利蜂,而紫红色花植株稳定且访花频率较高的传粉者有散熊蜂、白脸条蜂、意大利蜂和海切叶蜂。传粉昆虫在白色花上的单花停留时间比紫红色花的稍长,两者存在显著差异。 4. 羊柴白色花植株和紫红色花植株自花授粉的结实率(白色花:4.31±0.34%;紫红色花:4.58±0.53%),相对于人工异花授粉的结实率(白色花:19.77±2.31%;紫红色花:21.03±3.02%)较低。自然结实率(白色花:25.93±2.30%;紫红色花:25.24±1.61%)没有显著性差异(F=0.25;P=0.80)。此外,羊柴不存在无融合生殖现象。 5. 角蒿花期从7月中旬持续到9月初,单花开放时间为5-9h;单花花粉量为18816.27±326.70、在花开放后3-4h时,花粉活力达到最大值71.98±1.23%,胚珠数为180.80±5.30,P/O值为104.7。在花开放后3-4h时,花蜜量达到最大值1.41±0.35ul。角蒿的传粉昆虫仅有散熊蜂和四条无垫蜂。在花开放过程中,花粉活力动态和花蜜分泌动态都与传粉昆虫的行为不吻合。 6. 角蒿自花授粉和人工异花授粉的结实率和结籽率均无显著差异。自然结实率为85.93±1.63%,显著地低于自花授粉和人工异花授粉,但是,自花授粉、人工异花授粉及自然对照的结籽率无显著差异。在开放传粉的情况下,被去雄的花结实率仅为48.90±5.37%,说明昆虫传粉仅贡献一部分结实率。角蒿不存在无融合生殖。
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Mode of access: Internet.
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Mode of access: Internet.
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Mode of access: Internet.
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Pyrrolizidine alkaloids (PAs) are a group of plant secondary metabolites with carcinogenic and hepatotoxic properties. When PA-producing plants contaminate crops, toxins can be transferred through the food chain and cause illness in humans and animals, most notably hepatic veno-occlusive disease. Honey has been identified as a direct risk of human exposure. The European Food Safety Authority has recently identified four groups of PAs that are of particular importance for food and feed: senecionine-type, lycopsamine-type, heliotrine-type and monocrotaline-type. Liquid or gas chromatography methods are currently used to detect PAs but there are no rapid screening assays available commercially. Therefore, the aim of this study was to develop a rapid multiplex ELISA test for the representatives of three groups of alkaloids (senecionine, lycopsamine and heliotrine types) that would be used as a risk-management tool for the screening of these toxic compounds in food and feed. The method was validated for honey and feed matrices and was demonstrated to have a detection capability less than 25 µg/kg for jacobine, lycopsamine, heliotrine and senecionine. The zinc reduction step introduced to the extraction procedure allows for the additional detection of the presence of N-oxides of PAs. This first multiplex immunoassay for PA detection with N-oxide reduction can be used for the simultaneous screening of 21 samples for >12 PA analytes. Honey samples (n?=?146) from various origins were analysed for PA determination. Six samples were determined to contain measurable PAs >25 µg/kg by ELISA which correlated to >10 µg/kg by LC-MS/MS.
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Isolates of Armillaria mellea and A. gallica that differed in virulence to healthy blackcurrant, strawberry, Lawson cypress and privet were used to inoculate plants exposed to different watering regimes. Host plants from which water had either been withheld or their roots kept constantly flooded with water, both showed increased susceptibility compared to those plants, which had been watered regularly. At the end of the period of stress, roots from randomly selected plants from each treatment were harvested. Following chemical analysis of the roots for protein, lipids, and carbohydrates including starch, in vitro assays were carried out with these substances. The increased amounts of these nutrients in both groups of stressed plants are sufficient to stimulate the growth of both A. mellea and A. gallica and enhance their virulence.
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The diversity and abundance of wild insect pollinators have declined in many agricultural landscapes. Whether such declines reduce crop yields, or are mitigated by managed pollinators such as honey bees, is unclear. We found universally positive associations of fruit set with flower visitation by wild insects in 41 crop systems worldwide. In contrast, fruit set increased significantly with flower visitation by honey bees in only 14% of the systems surveyed. Overall, wild insects pollinated crops more effectively; an increase in wild insect visitation enhanced fruit set by twice as much as an equivalent increase in honey bee visitation. Visitation by wild insects and honey bees promoted fruit set independently, so pollination by managed honey bees supplemented, rather than substituted for, pollination by wild insects. Our results suggest that new practices for integrated management of both honey bees and diverse wild insect assemblages will enhance global crop yields.
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The Maya of the Yucatan region have a long history of keeping the native stingless bees (subfamily Meliponinae). However, market forces in the last few decades have driven the Maya to favor the use of invasive Africanized honey bees (Apis mellifera scutellata) for producing large quantities of high quality honey that has an international market. Furthermore, the native bees traditionally used by the Maya are now disappearing, along with the practice of keeping them. ^ An interdisciplinary approach was taken in order to determine the social factors behind the decrease in stingless beekeeping and the ecological driving forces behind their disappearance from the wild. Social research methods included participant observation with stingless beekeepers, Apis beekeepers, and marketing intermediaries. Ecological research methods included point observations of commonly known melliferous and polliniferous plants along transects in three communities with different degrees of human induced ecosystem disturbance. ^ The stingless bee species most important to the Maya, Melipona beecheii, has become extremely rare, and this has caused a breakdown of stingless beekeeping tradition, compounded with the pressure of the market economy, which fuels Apis beekeeping and has lessened the influence of traditional practices. The community with the heaviest amount of human induced ecosystem disturbance also had the highest degree of dominance of Apis mellifera, while the area with the most intact ecosystem had the highest diversity of stingless bees, though Apis mellifera was still the dominant species. Aggressive competitive behavior involving physical attacks by Apis mellifera against stingless bees was observed on several occasions, and this is a new observation previously unreported by science. ^
Error, Bias, and Long-Branch Attraction in Data for Two Chloroplast Photosystem Genes in Seed Plants
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Sequences of two chloroplast photosystem genes, psaA and psbB, together comprising about 3,500 bp, were obtained for all five major groups of extant seed plants and several outgroups among other vascular plants. Strongly supported, but significantly conflicting, phylogenetic signals were obtained in parsimony analyses from partitions of the data into first and second codon positions versus third positions. In the former, both genes agreed on a monophyletic gymnosperms, with Gnetales closely related to certain conifers. In the latter, Gnetales are inferred to be the sister group of all other seed plants, with gymnosperms paraphyletic. None of the data supported the modern ‘‘anthophyte hypothesis,’’ which places Gnetales as the sister group of flowering plants. A series of simulation studies were undertaken to examine the error rate for parsimony inference. Three kinds of errors were examined: random error, systematic bias (both properties of finite data sets), and statistical inconsistency owing to long-branch attraction (an asymptotic property). Parsimony reconstructions were extremely biased for third-position data for psbB. Regardless of the true underlying tree, a tree in which Gnetales are sister to all other seed plants was likely to be reconstructed for these data. None of the combinations of genes or partitions permits the anthophyte tree to be reconstructed with high probability. Simulations of progressively larger data sets indicate the existence of long-branch attraction (statistical inconsistency) for third-position psbB data if either the anthophyte tree or the gymnosperm tree is correct. This is also true for the anthophyte tree using either psaA third positions or psbB first and second positions. A factor contributing to bias and inconsistency is extremely short branches at the base of the seed plant radiation, coupled with extremely high rates in Gnetales and nonseed plant outgroups. M. J. Sanderson,* M. F. Wojciechowski,*† J.-M. Hu,* T. Sher Khan,* and S. G. Brady