利用人工饲料养蚜虫的技术

对利用人工饲料饲养蚜虫的方法、人工饲料类型及其组成做了介绍．概述了利用人工饲料饲养蚜虫的效果．并结合献报道和作本人经历．讨论了影响蚜虫人工饲料饲养效果的关键因子及改进方法。     

稻纵卷叶螟的人工饲养技术

稻纵卷叶螟Cnaphalocrocis medinalis的人工饲养技术是科研人员顺利开展相关研究工作的前题.稻纵卷叶螟人工饲养所要解决和重视的关键问题是食料和饲养条件.目前主要以天然食料、人工饲料以及2种食料相结合的方法饲养稻纵卷叶螟.而饲养条件,如温湿度、饲养密度、化蛹介质、产卵介质等会对对稻纵卷叶螟的生长发育产生影响.本文对目前我国稻纵卷叶螟人工饲料及人工饲养技术进行综述,有助于厘清该虫人工饲养技术的发展脉络,促进人工饲养技术的改善和提高,推动我国稻纵卷叶螟的研究.     

稻纵卷叶螟的人工饲养技术

稻纵卷叶螟Cnaphalocrocis medinalis的人工饲养技术是科研人员顺利开展相关研究工作的前题.稻纵卷叶螟人工饲养所要解决和重视的关键问题是食料和饲养条件.目前主要以天然食料、人工饲料以及2种食料相结合的方法饲养稻纵卷叶螟.而饲养条件,如温湿度、饲养密度、化蛹介质、产卵介质等会对对稻纵卷叶螟的生长发育产生影响.本文对目前我国稻纵卷叶螟人工饲料及人工饲养技术进行综述,有助于厘清该虫人工饲养技术的发展脉络,促进人工饲养技术的改善和提高,推动我国稻纵卷叶螟的研究.     

稻纵卷叶螟的人工饲养技术

稻纵卷叶螟Cnaphalocrocis medinalis的人工饲养技术是科研人员顺利开展相关研究工作的前题.稻纵卷叶螟人工饲养所要解决和重视的关键问题是食料和饲养条件.目前主要以天然食料、人工饲料以及2种食料相结合的方法饲养稻纵卷叶螟.而饲养条件,如温湿度、饲养密度、化蛹介质、产卵介质等会对对稻纵卷叶螟的生长发育产生影响.本文对目前我国稻纵卷叶螟人工饲料及人工饲养技术进行综述,有助于厘清该虫人工饲养技术的发展脉络,促进人工饲养技术的改善和提高,推动我国稻纵卷叶螟的研究.     

同翅目昆虫人工饲料饲养技术

本文从人工饲料的组成与类型、饲养方法及饲养结果等方面总结了同翅目昆虫人工饲料饲养技术的研究现状 ,并简要讨论了其存在的问题和改进方法。     

茶尺蠖人工饲料的研究

本报道饲养茶尺蠖(Ectropis obliqua hypulina Wehrli)的5种人工饲料及其饲养方法．5种人工饲料均可用于大规模饲养一代幼虫．其中62号配方可用于续代饲养,在实验室内饲养5代的结果表明。效果良好．在饲料成分的加工．配制及饲养方法等方面．较前人有相当大的改进,因而叶因子用量减少,幼虫历期缩短．用人工饲料饲养的幼虫历期为13-20天。基本接近以茶叶饲养的对照(11—18天)．实验结果还表明饲料含水量．饲养方法．饲养密度和添加饲料的次数不同,对茶尺蠖的生长发育有明显的影响．初龄幼虫用平面培养基倒置饲养和高龄幼虫用片状饲料正置饲养为最佳方法．     

介绍红火蚁的野外采集和实验室饲养的方法

介绍了红火蚁Solenopsis invictaBuren的田间采集、蚁群分离和实验室饲养和操作方法及红火蚁人工饲料的制备,结合实验室饲养经验描述了日常红火蚁饲养所需设备和器具,简述红火蚁饲养的关键技术和注意事项。为开展红火蚁的生物学、生态学和药剂筛选提供切实可行的方法。     

家蚁的人工饲养方法

<正> 家蚁的人工饲养是研究其生物学、生态学、生理学以及防冶的基础。笔者于1984～1989年在西南农业大学作研究生论文期间,摸索出了比较适合各种不同目的和用途的蚂蚁饲养方法,现作简要介绍。 一、饲养方法 饲养方法一 用木料或泡沫塑料做成图:(?)形式的人工巢,再用大小两个瓷盘(31×41     

人工饲养鳄蜥的潜水行为及影响因素

性能是有机体完成某些生态相关任务的定量指标,自愿潜水的最长潜水持续时长是量化潜水性能的重要指标。鳄蜥（Shinisaurus crocodilurus）作为一种濒危的半水生蜥蜴,常将潜水行为作为避敌策略。2021年7至8月,人为干扰（不直接触碰）广西大桂山鳄蜥国家级自然保护区人工饲养的鳄蜥,摄像记录其相应的潜水行为,利用Pearson相关分析、单因素方差分析、一般线性模型、一元线性回归及逐步回归5种方法分析了25只亚成体、19只成体雌性、17只成体雄性共61只人工饲养鳄蜥的潜水行为及影响因素。结果表明,人工饲养鳄蜥的潜水行为具有可重复性。不同性别和年龄的人工饲养鳄蜥的最长潜水持续时长没有差异,人工饲养鳄蜥潜水时的行为不影响其最长潜水持续时长,温度也不影响人工饲养鳄蜥的最长潜水持续时长。人工饲养鳄蜥的最长潜水持续时长与尾长、尾部体积呈负相关,与尾部损失呈正相关。本研究结果表明,人工饲养鳄蜥的潜水性能受到尾部特征的影响,潜水性能和游泳性能之间可能发生了权衡。     

云眼斑螳的人工饲养和繁殖

介绍了观赏昆虫云眼斑螳的形态、习性以及在北方人工饲养、繁殖的方法和饲养过程中应注意的问题等.     

Breeding seasons of sea-birds in the Galapagos Islands

The sea-birds breeding in the Galapagos Islands show a diversity of breeding cycles. Some species have rigidly fixed annual breeding while others breed throughout the year but have peaks of breeding at less than annual intervals. The eight species which have non-annual breeding are probably breeding as often as possible with the interval between the end of a breeding attempt and the start of the next being the time needed to moult the wing and tail feathers. Only one species is definitely known to breed and moult at the same time.
Although there are well marked seasonal fluctuations in the sea temperature, regular sampling failed to demonstrate any regular fluctuations in the surface plankton. The available evidence suggests that food for some sea-birds is erratic and unpredictable. Some non-annual breeding species have their breeding synchronized by severe food shortages which delay breeding, presumably because females cannot find enough food to form eggs, until conditions improve.
Timing of the breeding season in annual breeders is less easily explained but some species may be feeding well away from the islands in areas where there is a regular fluctuation in the food supply. Most of the annual breeders have prolonged breeding seasons and in two species breeding is out of phase on different islands. Perhaps species are influenced by some weak annual variation in food supply which makes it disadvantageous to breed in a few months of the year.     

Life stage specific variation in the occupancy of ponds by Litoria aurea,a threatened amphibian

Breeding aggregations are a reproductive strategy to increase mate finding opportunity. However, because aggregations skew the distribution of mature animals through conspecific attraction, rather than resource availability, the distribution of breeding sites may be reduced, so that not all suitable breeding sites are used. To examine the relationship between landscape and reproductive strategies of a threatened frog, Litoria aurea, we studied its distribution at Sydney Olympic Park over two breeding seasons. We aimed to: (i) determine the distribution and predictors of breeding ponds; and (ii) assess the significance of dispersal in the juvenile age‐class. We found that the distribution of the calling males was highly skewed and occurred in large, well‐connected ponds. Despite this, breeding ponds were not aggregated; pond size was the single factor explaining the distribution of breeding ponds. Juvenile frogs dispersed from breeding ponds and were not associated with a specific pond characteristic. Less breeding occurred in the second season during which fewer ponds were used for breeding including many different ponds from the previous year. These changes suggest that breeding effort and breeding pond choice are dynamic and therefore knowledge of the factors that drive breeding events will be a powerful tool in managing species, particularly in light of changing climatic regimes.     

花卉育种技术研究进展(综述)

本文综述近年来国内外花卉育种技术及成果。常规育种仍是花卉育种的主要方法,但日益成熟的生物技术为花卉育种提供了新的途径,尤其是基因工程在改良花卉的色、香、形及延缓衰老等方面将发挥重要作用。     

Cooperative breeding in birds: the role of ecology

Theory predicts that cooperative breeding should only occurin species in which certain individuals are constrained frombreeding independently by some peculiarity of the species' ecology.Here, we use comparative methods to examine the role of variationin ecology in explaining differences between taxa in the frequencyof cooperative breeding. We address three questions. First,does the frequency of cooperative breeding vary at just one phylogeneticlevel, or across several levels? Second, are differences inthe frequency of cooperative breeding among closely-relatedspecies correlated with ecology? Last, are ecological differencesbetween ancient lineages important in predisposing certain lineagesto cooperative breeding? We find that variation in the frequencyof cooperative breeding occurs across all phylogenetic levels,with 40% among families and 60% within families. Also, variationin the frequency of cooperative breeding between closely related speciesis associated with ecological differences. However, differencesin the frequency of cooperative breeding among more ancientlineages are not correlated with differences in ecology. Together,our results suggest that cooperative breeding is not due toany single factor, but is a two step-process: life-history predispositionand ecological facilitation. Low annual mortality predisposescertain lineages to cooperative breeding. Subsequently, changesin ecology facilitate the evolution of cooperative breedingwithin these predisposed lineages. The key ecological changesappear to be sedentariness and living in a relatively invariableand warm climate. Thus, although ecological variation is notthe most important factor in predisposing lineages to cooperativebreeding, it is important in determining exactly which speciesor populations in a predisposed lineage will adopt cooperativebreeding.     

Influence of Winter Ranging Behaviour on the Social Organization of a Cooperatively Breeding Bird Species, The Apostlebird

Most cooperative breeding bird species live in family groups that are formed through the prolonged association of offspring with their parents. Research into cooperative families has in particular investigated the balance between cooperation and conflict over reproductive decisions. As a consequence of this research focus, social interactions among group members outside the breeding season are rarely studied, despite the fact that they are likely to be crucial for social decisions. We investigated the social dynamics and ranging behaviour of the family group living cooperatively breeding apostlebird ( Struthidea cinerea ) outside the breeding season. Group size changed between, but not within, the seasons, being smaller during the breeding season than in the winter season. This change in group size was a consequence of breeding groups merging after breeding, then splitting again before the next breeding season. While breeding groups used small, non-overlapping home ranges (      = 113 ha) around the nesting site, during winter groups moved up to 1200 ha (      = 598 ha), and interacted frequently with up to four other winter groups. In particular large groups often joined together during winter and spent up to 50% of their time associating with other large winter groups. This apparent fission-fusion system facilitated the exchange of group members, offering the possibility to form new breeding coalitions and new groups. The results of this study suggest that behaviour outside the breeding season can be of considerable importance to the social dynamics of both families and cooperative breeding in such systems.     

Climatic effects on timing of spring migration and breeding in a long-distance migrant, the pied flycatcher Ficedula hypoleuca

Climate change has advanced the breeding dates of many bird species, but for few species we know whether this advancement is sufficient to track the advancement of the underlying levels of the food chain. For the long-distance migratory pied flycatcher Ficedula hypoleuca the advancement in breeding time has been insufficient to maintain the synchrony with their main food sources. The timing of arrival in the breeding areas from their African wintering grounds is likely to constrain the advancement of breeding date. We hypothesise that this is because in Africa they cannot predict the advancement of spring in their breeding habitat. However, long-distance migrants may advance their arrival time by migrating faster when circumstances en route are favourable. In this study we show that both arrival and breeding date depend on temperatures at their main North African staging grounds, as well as on temperature at the breeding grounds. Male arrival and average laying date were not correlated, but the positive effect of temperature in North Africa on breeding dates suggests that breeding date is indeed constrained by arrival of females. Long-distance migrants thus are able to adjust arrival and hence breeding by faster spring migration, but the degree of adjustment is probably limited as timing schedules in spring are tight. Furthermore, as climate change is affecting temperatures differently along the migratory flyway and the breeding areas, it is unlikely that arrival dates are advanced at the same rate as the timing of breeding should advance, given the advancement of the underlying levels of the food chain.     

Carry-over effects from passage regions are more important than breeding climate in determining the breeding phenology and performance of three avian migrants of conservation concern

Long distance migrants are declining more rapidly than residents, with birds that breed in Europe and winter in tropical Africa providing particularly clear examples. Causal mechanisms may include climate change, but are poorly understood partly because carry-over effects from non-breeding ranges can influence breeding performance. Using long-term data spanning four decades we assess how climatic variation in migrants’ winter, passage and breeding ranges determine timing of breeding and reproductive success. We do so for three Afro-European avian migrants of regional conservation concern (redstart, spotted flycatcher and wood warbler). We find that carry-over effects from passage regions consistently had stronger impacts on breeding phenology than breeding climate. Warm Mediterranean passage conditions promoted earlier breeding in all species, and redstarts also bred earlier following higher Sahel rainfall. Warmer springs on the breeding grounds promoted slightly earlier breeding in redstart and wood warbler, but not spotted flycatcher. Carry-over effects also typically influenced breeding performance to a greater extent than weather on the breeding grounds. Greater rainfall in the Sahel increased redstart brood size, warmer Mediterranean passage conditions increased spotted flycatcher brood size and, to a lesser extent, the number of wood warbler fledglings. In contrast to the concern regarding climate change impacts on migrants’ breeding grounds we found no evidence that warmer temperatures on the breeding grounds were associated with reduced reproductive performance. We thus find that climatic variation on the non-breeding grounds, especially passage regions, typically influenced migrants’ breeding phenology and demography more strongly than equivalent variation on the breeding sites. Such carry-over effects should be considered when assessing the causes of migrants’ marked population declines.     

Winter commingling of populations of migratory species can cause breeding range underpopulation

We build a model with large-scale demographic consequences for migratory species. The model operates where four elements co-occur, and we rely on empirical research using migratory birds to demonstrate them. First, breeding ranges have internal structure flowing from natal philopatry. Second, fecundity varies geographically. Third, populations of different breeding provenances commingle during winter. And fourth, a population-limiting carrying capacity operates during winter. In the absence of breeding season population-limitation, only the breeding population with maximum fecundity persists. Consequently, some potential breeding areas that offer suitable and productive habitat are bereft of breeding birds because of the interplay between the geographical fecundity gradient and the shared winter quarters. Where breeding season population-limitation also plays a role for at least one population, one (or more) breeding population becomes permanently depressed, resulting in a density well below the carrying capacity of the productive breeding habitat that is occupied. In either case, not all populations fare equally well, despite net positive breeding season productivity. Changes in winter carrying capacity, for example habitat degradation in winter quarters, can lead to uneven effects on geographically defined breeding populations, even though there has been no change in the circumstances of the breeding range.     

Non‐breeding range size predicts the magnitude of population trends in trans‐Saharan migratory passerine birds

Understanding why populations of some migratory species show a directional change over time, i.e. increase or decrease, while others do not, remains a challenge for ecological research. One possible explanation is that species with smaller non‐breeding ranges may have more pronounced directional population trends, and their populations are thus more sensitive to the variation in environmental conditions in their non‐breeding quarters. According to the serial residency hypothesis, this sensitivity should lead to higher magnitudes (i.e. absolute values) of population trends for species with smaller non‐breeding ranges, with the direction of trend being either positive or negative depending on the nature of the environmental change. We tested this hypothesis using population trends over 2001–2012 for 36 sub‐Saharan migratory passerine birds breeding in Europe. Namely, we related the magnitude of the species' population trends to the size of their sub‐Saharan non‐breeding grounds, whilst controlling for factors including number of migration routes, non‐breeding habitat niche and wetness, breeding habitat type and life‐history strategy. The magnitude of species' population trends grew with decreasing absolute size of sub‐Saharan non‐breeding ranges, and this result remained significant when non‐breeding range size was expressed relative to the size of the breeding range. After repeating the analysis with the trend direction, the relationship with the non‐breeding range size disappeared, indicating that both population decreases and increases are frequent amongst species with small non‐breeding range sizes. Therefore, species with small non‐breeding ranges are at a higher risk of population decline due to adverse factors such as habitat loss or climatic extremes, but their populations are also more likely to increase when suitable conditions appear. As non‐breeding ranges may originate from stochasticity of non‐breeding site selection in naive birds (‘serial‐residency’ hypothesis), it is crucial to maintain a network of stable and resilient habitats over large areas of birds’ non‐breeding quarters.     

Range sizes and habitat use of non‐breeding Crested Caracaras in Florida

In Florida, habitats that include the breeding territories of Crested Caracaras (Caracara cheriway) are protected, but non‐breeding individuals may be vulnerable because they may occupy different areas and habitats. We captured and radio‐tagged 58 non‐breeding caracaras in Florida from July 2006–March 2009, determined their locations during weekly flights, and used GIS and compositional analysis to evaluate range sizes and habitat use. Non‐breeding caracaras (N = 58) ranged five times more widely during breeding seasons (N = 573 locations) than during non‐breeding seasons (N = 592 locations), and ranged >250 times more widely than breeding caracaras that defend territories year‐round. The large ranges of non‐breeders suggest they may be searching for and evaluating prospective territories or breeding opportunities (territory prospecting). Pasture occupied by cattle was the most used habitat relative to availability and was used more than pasture without cattle, likely because insects associated with cattle are an important food source for caracaras. Cattle numbers in Florida are declining and, because both breeding and non‐breeding caracaras primarily occupy pasture, this may present difficulties for long‐term management. Citrus groves were also used more than expected given availability by non‐breeding caracaras, but are rarely included in nesting territories. Because pasture and citrus were often adjacent, we suggest that citrus groves may function as refugia from socially dominant breeding caracaras. Conservation and recovery efforts for Florida's caracara population are needed throughout the range of non‐breeders, and should include management that ensures availability of habitat matrices of cattle pasture and citrus groves.