大蜜蜂的生物学特性、面临威胁与保护策略

昆虫传粉在维持植物的有性繁殖、物种形成及生态系统稳定中扮演着重要角色, 而野生传粉昆虫为生态系统提供了巨大的传粉服务功能。大蜜蜂(Apis dorsata)为亚洲特有的一种野生传粉昆虫, 是热带地区多种植物和农作物的有效传粉者, 在保障热带生物多样性及作物产量中有不可或缺的作用。但受全球气候变化、人类活动和生境恶化等因素的影响, 其种群数量日益减少, 开展大蜜蜂种质资源保护势在必行。本文综述了大蜜蜂筑巢、迁飞和传粉服务功能, 分析了人为猎取蜂巢, 栖息生境遭受破坏, 杀虫剂和除草剂滥用, 昆虫、螨类和病原物侵染, 气候变化等威胁种群的因素, 以期从强化大蜜蜂基础研究和保护、推动生态农业发展、建立适合大蜜蜂迁飞生态廊道、加强检验检疫及科学合理利用大蜜蜂种质资源等方面制定相应的保护措施。     

荒山绿化对野生新疆郁金香传粉昆虫多样性的影响

为探究荒山绿化模式下对野生新疆郁金香Tulipa sinkiangensis传粉昆虫多样性的影响,选取乌鲁木齐市雅玛里克山设置长期绿化区、短期绿化区和自然生境3个环境梯度,采取样线和样方调查等方法进行新疆郁金香传粉昆虫多样性的研究。共收集传粉昆虫共316头,隶属17科23属36种,优势种为黑腹膝芒寄蝇Gonia picea。不同绿化梯度下物种丰富度指数相似,但随着荒山绿化进程的推进传粉昆虫多样性指数、均匀度指数呈下降趋势,自然生境最高(2.719;0.941),长期绿化区最低(1.299±0.311;0.553±0.076)。长期绿化区和短期绿化区之间物种组成极不相似;长期绿化区和自然生境以及短期绿化区和自然生境之间物种组成均为中等不相似。同时发现,树木胸径对传粉昆虫多样性具有显著负面影响(P=0.047)。研究表明,未来荒山绿化工程应提高生态异质性,避免大片纯林的单一种植模式。     

风筝果镜像花的雌雄异位变化及传粉生态型的形成

亚洲特有植物风筝果(Hiptage benghalensis)镜像花(mirror-image flowers)的雌雄异位变化极大, 柱头与可育花药的空间距离在海南岛与云南西双版纳种群仅有2-4 mm, 而在贵州及云南东南部种群可达10-12 mm。为验证 “镜像花雌雄异位的变化是各个地理种群受到传粉昆虫体型大小选择的结果”假说, 本文开展了传粉生态学与分子生物学研究, 探讨风筝果不同地理种群的雌雄异位变化是否与当地传粉者体型相关, 是否有着遗传基础, 以及是否形成了“传粉生态型”(pollination ecotype)。结果表明, 雌雄异位程度大的贵州种群和云南东南部种群, 其传粉者也是体型较大的木蜂(Xylocopa nasalis)和熊蜂一种(Bombus sp.); 雌雄异位程度小的海南岛种群和云南西双版纳种群的传粉者则是体型较小的大蜜蜂(Apis dorsata)、西方蜜蜂(A. mellifera)。除了雌雄异位的明显分化(F = 53.69, P < 0.01)之外, 花柱长度也在这两类种群之间差异显著(F = 12.5, P < 0.05), 与传粉昆虫身体长度密切相关。通过叶绿体ycf1b、rbcL和细胞核ITS 3个DNA片段的序列分析, 由大型蜂传粉的雌雄异位程度较大的3个种群(贵州和云南东南部种群)遗传关系极近, 与小型蜂传粉种群(雌雄异位较小的海南岛种群和云南西双版纳种群)存在明显的遗传分化。这些结果显示, 风筝果不同地理种群的镜像花雌雄异位程度的变化可能是适应局域不同体型大小的传粉昆虫的选择结果, 而且种群间出现了基因流的隔断, 可能与大型蜂、小型蜂传粉的两种生态型有关。镜像花通过雌雄异位的变化适应不同地域的传粉者而形成传粉生态型, 这种传粉生态型及其传粉隔离机制可能是风筝果属物种形成与维持的一个重要原因。     

野生蜜蜂及其传粉作用的研究现状

传粉是维持与提升生物多样性的重要生态过程。膜翅目蜜蜂总科昆虫是自然界中最重要的传粉者, 但对野生蜜蜂的研究一直以来非常薄弱, 如野生蜜蜂类群的资源调查、种类的准确鉴别、营巢生物学与传粉生物学研究等方面。目前, 生物多样性与保护生物学方面的工作越来越多地涉及野生蜜蜂与植物的相互关系, 地方植物区系与农林作物的传粉生物学基础研究与应用项目也引起重视。本文综述了国内外野生蜜蜂的研究现状, 期望从分类学、营巢生物学与传粉生物学等方面推动野生蜜蜂传粉在农林业生产实践中的应用。     

北京昌平区景观复杂度和局地管理对苹果园传粉蜂多样性的影响

传粉蜂为作物生产和粮食安全提供重要的生态系统服务。随着农业经济的不断发展,土地利用强度加剧,大量自然或半自然生境已经转变为农业用地。景观均质化和集约化管理导致野生蜂多样性下降,从而威胁到农业可持续生产。本研究以北京市昌平区苹果园为对象,探究景观复杂度(半自然生境比例)、局地管理强度(地表开花植物多样性和土壤全氮)及其交互作用对传粉蜂多样性的影响。结果表明: 共捕获传粉蜂8642头,其中人工蜂5125头,野生蜂分属5科14属49种3517头。传粉蜂多样性对景观复杂度和局地管理强度响应的最优尺度在500 m。样点半径500 m范围内,总传粉蜂和野生蜂多度随周围半自然生境增加均呈显著上升趋势。景观复杂度与开花植物多样性的交互作用对总传粉蜂和野生蜂物种丰富度有显著影响。当景观复杂度较低时(≤29.9%),总传粉蜂和野生蜂物种丰富度与开花植物多样性呈显著正相关;而当景观复杂度较高时(>29.9%),总传粉蜂和野生蜂物种丰富度与开花植物多样性呈显著负相关。此外,人工蜂多度随果园内局地开花植物多样性和土壤全氮增加呈显著升高趋势。土壤全氮与开花植物多样性的交互作用对人工蜂多度有显著影响。当土壤全氮含量较低时(≤1.9 g·kg^-1),人工蜂多度与开花植物多样性呈显著正相关;而当土壤全氮含量较高时(>1.9 g·kg^-1),人工蜂多度与开花植物多样性呈显著负相关。农业景观中半自然生境比例的增加有利于提高野生蜂多度,而地表开花植物多样性可以促进传粉蜂多样性,但是受到景观尺度(半自然生境比例)和局地尺度(氮肥施用)的影响。因此,农业景观中野生蜂多样性的维持需要综合考虑多尺度因素来制定保护策略。尽可能保留更高比例的耕地仍然是生产的长期需求,而保持中等景观复杂度,增加地表开花植物多样性,减少氮肥施用量将是促进苹果园传粉蜂多样性的有效方式。     

海南凤仙花不同海拔种群的传粉生物学

凤仙花属(Impatiens)植物具有极为广泛的多样性和类型各异的特化传粉者, 被誉为“双子叶的兰花”, 受到众多传粉生物学家的关注。本文以海南特有种海南凤仙花(Impatiens hainanensis)为研究对象, 对3个不同海拔梯度的种群进行了开花生物学特性和开花物候、花器官结构、花粉活力和柱头活性、传粉者种类和访花行为及繁育系统的比较研究。结果表明: 单花花期4.10 ± 0.46 d, 雄性期和雌性期分别约为3.15 ± 0.24 d和0.95 ± 0.36 d; 种群开花峰期在8月初, 高海拔种群的花期高峰相对滞后。低、中海拔种群花粉活力呈现先升高后下降的趋势, 以开花第2 d花粉活力最高; 高海拔种群花粉活力随开花时间推移逐渐下降; 柱头活性随开花时间的推移而增强, 高海拔种群开花各天次均较低、中海拔种群低。主要传粉昆虫为黄黑无垫蜂(Amegilla leptocoma)和绿条无垫蜂(A. zonata), 低、中海拔种群以黄黑无垫蜂为主, 高海拔种群以绿条无垫蜂为主。未观察到自动自花授粉和无融合生殖现象, 人工授粉能明显增加坐果率(75-90%), 自然坐果率在高海拔种群相对较低(40-60%), 说明存在较强的传粉者限制。海南凤仙花的保护需要同时关注其有效传粉者的保护, 促进有效传粉昆虫在不同海拔种群之间的往来, 保证种群间的花粉流与种子流, 维持海南凤仙花的种群遗传多样性与有效种群大小。     

安徽羽叶报春的有效传粉昆虫及花朵密度和种群大小对传粉效果的影响

对濒危植物有效传粉昆虫种类及其传粉行为的主要影响因素进行研究是科学合理地制订保护措施,从而对该物种实施有效保护的一个前提条件.安徽羽叶报春Primula merrilliana为二年生草本,具二型花,是我国特有的珍稀濒危物种.本文对其有效传粉昆虫种类、传粉行为及花朵密度和种群大小对传粉效果的影响进行了研究.结果表明安徽羽叶报春的有效传粉昆虫为截形蜂虻Bombylius major和中华雏蜂虻Anastoechus chinensis,而不是先前认为的蓟马Thrips sp,.花朵密度和种群大小对传粉效果均有显著的影响.高密度的花朵可以提高对有效传粉昆虫的吸引力,传粉昆虫数/天、被访花朵数/天和平均每花的被访次数/天与样方花朵的密度呈正相关关系.柱头所接受的正配花粉数和总花粉数及正配花粉数所占的比例均随种群中植株数目的增加而增加.型比的偏离和传粉昆虫的缺乏可能是导致小种群中传粉不利的主要因素.     

两种生境间大花百合不同性别表型开花及传粉特征的差异

植物的花期物候与花部综合特征均体现了其对生存环境的适应, 是与周围生物及非生物环境长期适应进化产生的结果。大花百合(Lilium concolor var. megalanthum)野外种群中具有雄性植株和两性植株两种不同性别表型。该研究以人为干扰较弱的孤山屯湿地以及人为干扰较强的金川湿地的大花百合为材料, 通过对两种生境间不同性别表型植株的花期物候、花部综合特征以及主要传粉昆虫的访花行为进行比较研究, 探究大花百合的开花及传粉特征在两种生境间的差异。结果表明: 孤山屯湿地内大花百合种群的始花期、盛花期、末花期均早于金川湿地。孤山屯湿地内大花百合的雄性植株在初开时花粉活力高于金川湿地, 而两种生境间的大花百合两性植株的花粉活力总体变化趋势一致。孤山屯湿地内大花百合雄性植株初开时的花蜜含量较高, 而后缓慢下降; 而在金川湿地内则是先增长, 48 h后开始下降。孤山屯湿地内大花百合两性植株的花蜜含量在开花24 h后开始下降, 金川湿地内则是48 h后才开始下降。孤山屯湿地内大花百合无论是雄性植株还是两性植株, 糖含量达到峰值的时间均比金川湿地晚。两种生境中大花百合两性植株的柱头可授性均保持较高水平。两种生境分布的大花百合主要传粉昆虫为中华蜜蜂(Apis cerana)、蓝灰蝶(Everes argiades)和老豹蛱蝶(Argyronome laodice)。孤山屯湿地内中华蜜蜂及蓝灰蝶对大花百合的访花频率均显著低于金川湿地, 但老豹蛱蝶的访花频率显著高于金川湿地。3种访花昆虫中, 中华蜜蜂的访花效率最高, 蓝灰蝶与老豹蛱蝶起到补充授粉的作用。两种生境间大花百合花期物候和花部综合特征的变化与当地小气候和传粉昆虫数量有关, 这种变化是大花百合经过长期适应而产生的。     

外来西方蜜蜂放蜂密度对云南罗平本地传粉蜂群落结构及物种多样性的影响

【目的】近年来随着交通条件的改善,每年有大量西方蜜蜂Apis mellifera蜂场从全国各地赶到云南放蜂。本研究旨在揭示西方蜜蜂这一外来蜂种对云南本地传粉蜂种类、数量及其物种多样性的影响。【方法】采用马来氏网收集、调查了云南省罗平县西方蜜蜂高放蜂密度试验点(鲁特和走马田)、中放蜂密度试验点(外纳和下阿列)和低放蜂密度试验点(马把和下庄科)共6个试验点包括山林生境和农田生境的本地传粉蜂群落结构;并对比分析了不同放蜂密度、不同生境下各试验点传粉蜂物种多样性指数(H′)、均匀度指数(J′)及丰富度指数(Dm)之间的差异。【结果】采集到的1 715头本地传粉蜂隶属于10科53种,其中蜜蜂科(Apidae)、隧蜂科(Halictidae)和胡蜂科(Vespidae)为优势类群,东方蜜蜂Apis cerana和切淡脉隧蜂Lasioglossum excisum为优势种。在放蜂密度(试验点周围3 km范围内西方蜜蜂蜂群数量)为723～2 750群这一变动范围内,各试验点本地传粉蜂物种数量、个体数量均随西方蜜蜂放蜂密度的增大而减少,物种多样性指数(H′)及丰富度指数(Dm)也相应降低,但西方蜜蜂放蜂密度对本地传粉蜂均匀度指数(J′)没有影响。此外,在相同放蜂密度下,山林生境的本地传粉蜂物种多样性均显著高于农田生境。【结论】云南罗平本地传粉蜂的群落结构及物种多样性受西方蜜蜂放蜂密度的影响,在放蜂密度从723～2 750群这一变动范围内,放蜂密度越大,本地传粉蜂的个体数、物种数、多样性指数和丰富度指数越小。本研究结果为进一步研究合理控制西方蜜蜂放蜂密度以保护云南本地传粉蜂种的多样性提供了思路。     

芳香石豆兰的繁殖生态学

芳香石豆兰(Bulbophyllum ambrosia)是分布于我国南方石灰岩山热带季节性雨林中的一种常见附生兰科植物, 附着生长于岩石或树干上, 野外监测发现其自然不结实。对芳香石豆兰繁殖生态学的研究表明, 不同于石豆兰属其他具有蝇类传粉综合征的种类, 其花具有香味和花蜜, 中华蜜蜂(Apis cerana cerana)是芳香石豆兰唯一的有效传粉者, 具有较高的访问频率, 自然种群中有较高的花粉块移出率和柱头花粉块沉降率, 在中华蜜蜂的传粉过程中, 芳香石豆兰铰链结构的唇瓣起着重要作用。人工授粉试验表明, 芳香石豆兰自交授粉不结实, 异交授粉结实率达90%以上, 芳香石豆兰为自交不亲和的繁育系统。芳香石豆兰具有较强的克隆生长能力, 同一个体花期内有大量的花同时开放, 其传粉者中华蜜蜂平均单次访花(4.29 ± 0.40)朵( n= 66), 造成了严重的同株异花传粉。芳香石豆兰附生于石灰岩山顶岩石或树干上, 种群密度较低, 使得不同个体之间花粉交流困难, 自交不亲和的特性导致了芳香石豆兰自然不结实。本研究结果为开展芳香石豆兰的有效保护提供了依据。     

Seasonal trends in honey bee pollen foraging revealed through DNA barcoding of bee-collected pollen

Insectes Sociaux - Recent declines in the abundance and diversity of wild bee species have made it important to understand how introduced species such as honey bees contribute to pollinating native...     

Bumble bee abundance and richness improves honey bee pollination behaviour in sweet cherry

Pollination service in agricultural crops increases significantly with pollinator diversity and wild pollinator abundance. Differences in the foraging behaviour of pollinating insects are one of the reasons why pollinator diversity and abundance enhances crop pollination. Here, we focused on the foraging behaviour of honey bees and bumble bees in sweet cherry orchards. In addition, we studied the influence of bee diversity and abundance on the foraging behaviour of honey bees and bumble bees. Honey bees were found to visit fewer flowers than bumble bees. Bumble bees also showed a higher probability of changing trees between rows than honey bees. Both visitation rate and probability of row changes of honey bees increased with bumble bee diversity and with bumble bee abundance. We also found that the probability of row changes of honey bees increased with increasing bumble bee abundance. These effects of bumble bee richness and abundance on the pollination behaviour of honey bees can improve the pollination performance of honey bees in crops that depend on cross pollination. Our results highlight the higher pollination performance of bumble bees and the facilitative effect of wild pollinators to crop pollination.     

Small wild bee abundance declines with distance into strawberry crops regardless of field margin habitat

The preservation of pollinator habitat on croplands in the form of hedgerows, wildflower strips, and natural and semi-natural areas can help maintain and enhance wild bee populations in agricultural landscapes. However, there have been few comparisons of the effectiveness of different types of field-margin pollinator habitat in maintaining bee diversity and pollination of the focal crops. We compared wild bee abundance, species richness and community composition between strawberry crops bordered by hedgerows, and those bordered by larger expanses of natural land (forests). Strawberry is an ideal crop in which to investigate pollinator export from field margins as the rows are covered with straw, which reduces habitat for ground-nesting bees within the crop; thus, most wild pollinators need to enter the crop from the margins. We sampled bees in six strawberry fields with hedgerow margins and six strawberry fields with forested margins of at least 200 m in length, using a paired design. We examined strawberry pollen deposition at regular intervals into the fields, and the magnitude of pollinator export from the field margins towards the centre of the crops. We found that bees as a group were no more species-rich or abundant in crops bordered by forests than in crops bordered by hedgerows, although large-bodied bees were more abundant in the former than the latter. Regardless of field-margin type, we found that small wild bee abundance declined significantly from the edge to the centre of the crop, but honey bee (Apis mellifera L.) and large-bodied bee abundance did not. Strawberry pollen deposition also did not decline with distance into the crop. Although previous work indicates that small wild bees are more effective (yield-increasing) pollinators of strawberry on a per-visit basis, their limited foraging ranges suggest they may only pollinate areas near the crop margins, given typical field sizes in our area.     

Agricultural buffer zone thresholds to safeguard functional bee diversity: Insights from a community modeling approach

Wild bee species are important pollinators in agricultural landscapes. However, population decline was reported over the last decades and is still ongoing. While agricultural intensification is a major driver of the rapid loss of pollinating species, transition zones between arable fields and forest or grassland patches, i.e., agricultural buffer zones, are frequently mentioned as suitable mitigation measures to support wild bee populations and other pollinator species. Despite the reported general positive effect, it remains unclear which amount of buffer zones is needed to ensure a sustainable and permanent impact for enhancing bee diversity and abundance. To address this question at a pollinator community level, we implemented a process‐based, spatially explicit simulation model of functional bee diversity dynamics in an agricultural landscape. More specifically, we introduced a variable amount of agricultural buffer zones (ABZs) at the transition of arable to grassland, or arable to forest patches to analyze the impact on bee functional diversity and functional richness. We focused our study on solitary bees in a typical agricultural area in the Northeast of Germany. Our results showed positive effects with at least 25% of virtually implemented agricultural buffer zones. However, higher amounts of ABZs of at least 75% should be considered to ensure a sufficient increase in Shannon diversity and decrease in quasi‐extinction risks. These high amounts of ABZs represent effective conservation measures to safeguard the stability of pollination services provided by solitary bee species. As the model structure can be easily adapted to other mobile species in agricultural landscapes, our community approach offers the chance to compare the effectiveness of conservation measures also for other pollinator communities in future.     

Bee Preference for Native versus Exotic Plants in Restored Agricultural Hedgerows

Habitat restoration to promote wild pollinator populations is becoming increasingly common in agricultural lands. Yet, little is known about how wild bees, globally the most important wild pollinators, use resources in restored habitats. We compared bee use of native and exotic plants in two types of restored native plant hedgerows: mature hedgerows (>10 years from establishment) designed for natural enemy enhancement and new hedgerows (≤2 years from establishment) designed to enhance bee populations. Bees were collected from flowers using timed aerial netting and flowering plant cover was estimated by species using cover classes. At mature hedgerow sites, wild bee abundance, richness, and diversity were greater on native plants than exotic plants. At new sites, where native plants were small and had limited floral display, abundance of bees was greater on native plants than exotic plants; but, controlling for floral cover, there was no difference in bee diversity and richness between the two plant types. At both mature and new hedgerows, wild bees preferred to forage from native plants than exotic plants. Honey bees, which were from managed colonies, also preferred native plants at mature hedgerow sites but exhibited no preference at new sites. Our study shows that wild bees, and managed bees in some cases, prefer to forage on native plants in hedgerows over co‐occurring weedy, exotic plants. Semi‐quantitative ranking identified which native plants were most preferred. Hedgerow restoration with native plants may help enhance wild bee abundance and diversity, and maintain honey bee health, in agricultural areas.     

Railway Embankments as New Habitat for Pollinators in an Agricultural Landscape

Pollinating insect populations, essential for maintaining wild plant diversity and agricultural productivity, rely on (semi)natural habitats. An increasing human population is encroaching upon and deteriorating pollinator habitats. Thus the population persistence of pollinating insects and their associated ecosystem services may depend upon on man-made novel habitats; however, their importance for ecosystem services is barely understood. We tested if man-made infrastructure (railway embankments) in an agricultural landscape establishes novel habitats that support large populations of pollinators (bees, butterflies, hoverflies) when compared to typical habitats for these insects, i.e., semi-natural grasslands. We also identified key environmental factors affecting the species richness and abundance of pollinators on embankments. Species richness and abundance of bees and butterflies were higher for railway embankments than for grasslands. The occurrence of bare (non-vegetated) ground on embankments positively affected bee species richness and abundance, but negatively affected butterfly populations. Species richness and abundance of butterflies positively depended on species richness of native plants on embankments, whereas bee species richness was positively affected by species richness of non-native flowering plants. The density of shrubs on embankments negatively affected the number of bee species and their abundance. Bee and hoverfly species richness were positively related to wood cover in a landscape surrounding embankments. This is the first study showing that railway embankments constitute valuable habitat for the conservation of pollinators in farmland. Specific conservation strategies involving embankments should focus on preventing habitat deterioration due to encroachment of dense shrubs and maintaining grassland vegetation with patches of bare ground.     

Patterns and drivers of wild bee community assembly in a Mediterranean IUCN important plant area

Recent reports of pollinator declines have stirred interest in investigating the impacts of habitat exploitation on the conservation of pollinator and plant communities. An important prerequisite to tailor conservation action is to understand the drivers and patterns of species-rich communities, and how they change in space and time during a whole season. To account for this, we surveyed wild bees and flowering plants using standardized transects in 11 natural habitat fragments of an IUCN important plant area along the coast of Israel. We used phylogeny- and taxon-based methods of community structure analyses to study the assembly processes of bee communities, and investigated the effects of several landscape parameters on bee diversity using generalized linear models (GLMs). Our results illustrate that natural habitat sites comprised significantly higher species richness compared to disturbed habitat sites, and show that even the smallest habitat fragments harbored unique bee assemblages, with significant species replacement (turnover) found in both space and time. Our GLMs indicated that flower diversity, and semi-natural habitat within 500 m of habitat fragments were important drivers of bee diversity, but we found no evidence for a species—area relationship among sites. Finally, we document a case of phylogenetic overdispersion despite low species richness, which highlights the importance of accounting for phylogenetic diversity rather than only species richness to reach a more fine-grained understanding of pollinator diversity. This, in turn, is pivotal to developing conservation actions to protect these essential pollinators and their interaction with rare and endemic plant species in this highly threatened ecosystem.     

Impacts of the use of nonnative commercial bumble bees for pollinator supplementation in raspberry

Evidence for pollinator declines has led to concern that inadequate pollination services may limit crop yields. The global trade in commercial bumble bee (Bombus spp.) colonies provides pollination services for both glasshouse and open-field crops. For example, in the United Kingdom, commercial colonies of nonnative subspecies of the bumble bee Bombus terrestris L. imported from mainland Europe are widely used for the pollination of raspberries, Rubus idaeus L. The extent to which these commercial colonies supplement the services provided by wild pollinators has not been formally quantified and the impact of commercial bumble bees on native bees visiting the crop is unknown. Here, the impacts of allowing commercially available bumble bee colonies to forage on raspberry canes are assessed in terms of the yield of marketable fruit produced and the pollinator communities found foraging on raspberry flowers. No differences were found in the abundance, diversity, or composition of social bee species observed visiting raspberry flowers when commercial bumble bees were deployed compared with when they were absent. However, weight of marketable raspberries produced increased when commercial bees were present, indicating that wild pollinator services alone are inadequate for attaining maximum yields. The findings of the study suggests that proportional yield increases associated with deployment of commercial colonies may be small, but that nevertheless, investment in commercial colonies for raspberry pollination could produce very significant increases in net profit for the grower. Given potential environmental risks associated with the importation of nonnative bumble bees, the development of alternative solutions to the pollination deficit in raspberry crops in the United Kingdom may be beneficial.     

Response diversity of wild bees to overwintering temperatures

Biodiversity can provide insurance against environmental change, but only if species differ in their response to environmental conditions (response diversity). Wild bees provide pollination services to wild and crop plants, and response diversity might insure this function against changing climate. To experimentally test the hypothesis that bee species differ in their response to increasing winter temperature, we stored cocoons of nine bee species at different temperatures during the winter (1.5–9.5 °C). Bee species differed significantly in their responses (weight loss, weight at emergence and emergence date). The developmental stage during the winter explained some of these differences. Bee species overwintering as adults generally showed decreased weight and earlier emergence with increasing temperature, whereas bee species overwintering in pre-imaginal stages showed weaker or even opposite responses. This means that winter warming will likely affect some bee species negatively by increasing energy expenditure, while others are less sensitive presumably due to different physiology. Likewise, species phenologies will respond differently to winter warming, potentially affecting plant–pollinator interactions. Responses are not independent of current flight periods: bees active in spring will likely show the strongest phenological advances. Taken together, wild bee diversity provides response diversity to climate change, which may be the basis for an insurance effect.     

Foraging ecology of a local wild bee community in an abandoned Satoyama system in Kanazawa, Central Japan

Satoyama is a traditional land management system in Japan that emphasizes the importance of a harmonious relationship between humans and their environment. It has been in a state of abandonment and destruction since the late 1960s. In 2000, the Japanese government initiated a new environment policy encouraging the use of Satoyama in biodiversity reservation areas. Before the initiation of active restoration works, an assessment of the potential of the Satoyama system is needed. To assess this potential, a study that focused on the foraging ecology of wild bees in a small abandoned Satoyama terraced paddy was carried out from June to October 2003. A total of 372 foraging bees belonging to 35 species in nine families was collected: two species of social bee ( Apis cerana and Bombus diversus ) and two of solitary bee ( Lasioglossum japonicum and Lasioglossum ohei ) dominated. The foraging activities of wild bees were highly influenced by the requirement of food for the colony and the active time of solitary bees. In the study, most wild bees showed a strong preference for abundant flowering plant species that produced a large number of flowers ( Achyranthes japonica and Polygonum thunbergii ). The results showed that an abandoned Satoyama system was an agricultural system that benefited pollinating bees. Careful and planned restoration practices to increase the diversity of foraging resources, microenvironment diversity and potential nesting areas for wild bees are needed to improve the ability of the Satoyama system to support more diverse and abundant wild bee populations.