光肩星天牛对4种不同槭树科寄主植物的选择机制

用动态顶空采集法、TCT-GC-MS分析鉴定了复叶槭、五角枫、华北五角枫、挪威槭等4种槭树科植物挥发物的种类和相对含量,测定结果显示：4种植物的化学指纹图谱明显不同。“Y”型嗅觉行为测定结果表明,不同植物的挥发物对光肩星天牛的引诱效果不同：复叶槭对光肩星天牛的引诱效果最好,其次为五角枫,均达到了差异显著的程度,华北五角枫对光肩星天牛有引诱作用,但未达到显著程度,挪威槭对光肩星天牛既无引诱作用又无驱避作用。数据分析发现,五角枫、华北五角枫和挪威槭较复叶槭引诱作用差的原因可能与五角枫、华北五角枫中含有对光肩星天牛的驱避组分罗勒烯和反-2-己烯醇、挪威槭中含有对光肩星天牛的驱避组分（E）-1-戊烯-3-醇、反-2-己烯醇和trans-香叶基丙酮有关;在4种植物中醇类化合物、酮类和醛类化合物相对含量的排列顺序与植物的抗性顺序相同,而烷烃类和酯类化合物含量的排列顺序与植物的抗性顺序相反;复叶槭咬食程度轻的原因可能与其叶表面具有较少的表皮毛有关。     

光肩星天牛与星天牛种间竞争行为研究

光肩星天牛Anoplophora glabripennis和星天牛Anoplophora chinensis是我国两种重要的林业蛀干害虫,存在很多共同的寄主植物。为了阐明两种星天牛之间的物种竞争关系,本文采用行为观察试验,研究两种星天牛寄主危害部位、异种危害寄主识别和种间争斗行为等试验。结果显示,光肩星天牛和星天牛在寄主植物上的取食危害部位有很大差异,光肩星天牛主要取食寄主植物的枝条上部,取食面积为2 390.0 mm²,占整个寄主植物取食面积的69.3%,星天牛主要取食寄主植物的树干上部,取食面积为3 140.0 mm²,占整个寄主植物的96.6%;两种星天牛都能识别异种天牛危害过的寄主,对其具有显著的回避性,其中光肩星天牛对星天牛危害过的寄主取食量平均值为420.8 mm²,显著低于健康寄主取食量平均值2 518.8 mm²,同样,星天牛对光肩星天牛危害过的寄主取食量平均值为436.8 mm²,显著低于健康寄主取食量平均值1 803.5 mm²,而对同...     

光肩星天牛种组研究现状

评述了我国光肩星天牛种组种类的外部形态和外生殖器主要鉴别特征、寄主、地理分布、起源及其演化。光肩星天牛主要分布在山西吕粱山、太行山以东的广大平原地区 ,寄主广泛 ,主要有榆、复叶槭、杨、柳、五角枫等。黄斑星天牛主要分布在秦岭以北 ,山西吕粱山、太行山以西的陕甘宁地区 ,向东已扩展到河南、河北 ;主要危害杨树 ,也为害柳、榆。四川星天牛主要分布于秦岭以南的云、贵、川地区 ,主要危害柳树 ;在这里至今还没有发现光肩星天牛和黄斑星天牛。     

中国的光肩星天牛类群

该文讨论我国光肩星天牛Anoplophoraglabrlpennis(Motschulsky)类群的外部形态和外生殖器的主要鉴别特征,寄主、地理分布、起源及其演化。光肩星天牛主要分布在山西吕梁山、太行山以东的广大平原地区,寄主广泛,主要有榆、复叶槭、杨、柳、五角枫等。黄斑星天牛主要分布在秦岭以北,山西吕粱山太行山以西的陕甘宁地区,向东已扩展到河南、河北;主要为害杨树,也为害柳、榆。四川星天牛主要分布于秦岭以南的西部地区,北限在陕西太白山到甘肃天水一带;主要为害柳。在秦岭以北到天水之间是黄斑星天牛和四川星天牛的重叠分布区,山西太行山两侧南北走向的狭长地带是光肩星天牛和黄肩星天牛重叠分布区,两个狭长地带交会处,大约在秦岭以北的陕西和(或)山西境内有三个种的重叠分布区域.在云、贵、川地区广泛分布着四川星天牛,至今还没有发现光肩星天牛、黄斑星天牛和蓝角星天牛,后者应该是一个值得怀疑的种。     

光肩星天牛的脑部结构

通过Mallory和HE染色,对光肩星天牛Anoplophora glabnpenn脑部显微结构进行了观察.结果表明,光肩星天牛的脑由前脑、中脑、后脑三部分组成.前脑叶髓层包括一对蕈形体、一个中央体、一个脑桥体和一对附叶,其中每个蕈形体仅有一个帽状的蕈体冠.中脑触角叶较大,由九簇放射状排列的触角神经束组成,中央的一束较粗,说明其嗅觉发达.后脑较小.     

光肩星天牛种群间及其近缘种遗传关系的RAPD研究

利用RAPD技术对采自中国和美国的星天牛属Anoplophora 5个种及8个光肩星天牛Anoplophora glabripennis (Motschulsky)地理种群共13个样品进行了遗传相似性分析。选用了Operon公司生产的引物H系列20个,L系列20个,Q系列11个共51个引物,最后从40个引物中筛选出26个具有多态性的引物作为第一组用于星天牛属种间和光肩星天牛种群间分析,从31个引物中筛选出19个具有多态性的引物作为第二组单独用于光肩星天牛种群分析。根据第一组引物实验获得的RAPD聚类图及遗传距离表明,各个地理种群的光肩星天牛和黄斑星天牛A. nobilis都聚在一起,形成一个大的分枝,而四川星天牛A. freyi、楝星天牛A. horsfieldi和星天牛A. chinensis均在此分枝之外。来自美国纽约和芝加哥的光肩星天牛种群聚于中国光肩星天牛种群之外的另一个独立的分枝上。分布在我国宁夏、内蒙古和河北的光肩星天牛以及宁夏黄斑星天牛和山东、陕西的光肩星天牛分别聚在一起,而甘肃的光肩星天牛与甘肃的黄斑星天牛则聚于另一枝,且它们之间的遗传距离很近,仅为0.1324,说明这两者之间有着极其相近的亲缘关系,由此推断光肩星天牛和黄斑星天牛的差异很小,遗传关系难以区分,进一步证实了它们很可能是同一个种下的两个不同的型。第二组引物实验得到了相似的结果,来自中国的6个光肩星天牛种群全部聚于同一枝中并分成两小枝： 分布于我国宁夏、河北、山东、甘肃的光肩星天牛聚在一起,内蒙古和陕西的光肩星天牛则成另一枝,而分布于美国纽约和芝加哥的光肩星天牛仍聚于中国光肩星天牛种群之外的一个单独的分枝上。但是美国光肩星天牛与中国光肩星天牛之间的遗传距离最近的为0.4578, 最远的为0.5960。由此认为,本研究中采自美国的两个光肩星天牛种群的样本和采自中国的光肩星天牛种群的样本之间存在显著差异,遗传关系较远。有必要从中国和世界其他天牛分布地采集更多样本做进一步DNA 分析。     

松墨天牛和光肩星天牛染色体核型

以松墨天牛Monochamus alternatus Hope和光肩星天牛Anoplophora glabripennis Motschulsky为研究对象,以各种天牛的最适条件和最佳材料进行染色体的制备和观察。试验结果如下:松墨天牛的最佳试验材料为7日龄蛹的精巢或卵巢,染色体数目2n=20,性别决定机制为Xyp,有大型染色体5对,中型染色体4对,性染色体在其大小排列中位于最末位,为中型染色体,染色体组式为5L+4M+Xyp;光肩星天牛的最佳试验材料为初羽化成虫的精巢或卵巢,染色体数目2n=20,性别决定机制为Xyp,有大型染色体6对,中型染色体3对,性染色体在其大小排列中位于最末位,但也为中型染色体,染色体组式:6L+3M+Xyp。     

新疆主要造林树种对光肩星天牛的抗性

利用网室接种和树干套笼接种光肩星天牛Anoplophora glabripennis(Motschulsky)成虫的方法,于2005年～2006年在新疆光肩星天牛的发生疫区,进行10种主要造林树种对其抗性的测定试验。结果显示:2种接种试验结果基本一致,各试验树种都不同程度地受到光肩星天牛的危害,表现出不同的抗虫性。根据孵化幼虫数综合分析,判断出试验树种的抗性高低的顺序为:桑树、沙枣>胡杨、圆冠榆、新疆杨、白榆、箭杆杨>复叶槭、旱柳、馒头柳。另外根据网室内试验树种上出现的羽化孔判断,光肩星天牛在新疆巴音郭楞蒙古自治州1年发生1代。     

利用管氏肿腿蜂防治光肩星天牛技术研究

光肩星天牛Anoplophora glabripennis是我国重大的森林害虫,对我国造林绿化和林业生态工程建设造成了严重危害。由于其为蛀干害虫,隐蔽性生活,难以防治。利用天敌开展生物防治是控制天牛的重要措施,作者研究探讨了利用管氏肿腿蜂Sclerodermus guani防治光肩星天牛技术。测定了管氏肿腿蜂对光肩星天牛1～3龄幼虫的室内控制作用,研究了林间防治防治技术。结果表明,在室内试验条件下,管氏肿腿蜂由于是抑性外寄生性,其产卵之前的刺蛰可造成天牛幼虫直接死亡,对1、2、3龄幼虫的平均致死率分别为100％、92．10％和87．29％;可寄生3龄天牛幼虫。在管氏肿腿蜂防治光肩星天牛小幼虫的林间试验中,管氏肿腿蜂对光肩星天牛小幼虫的致死率为27．79％-37．87％,平均为32．51％,放蜂比例以蜂虫比8-10：1的寄生率最高。     

Prediction of the potential global distribution of the Asian longhorned beetle Anoplophora glabripennis (Coleoptera: Cerambycidae) under climate change

1. The Asian longhorned beetle (ALB) Anoplophora glabripennis (Motschulsky) (Coleoptera: Cerambycidae) is an important wood-boring pest that has caused substantial damage to broadleaf trees in Asia, North America, and Europe.
2. We used the modelling software CLIMEX to project the potential global distribution of ALB based on both historical (1987–2016) and future (2021–2050) climate conditions. ALB has possible hosts in 37 genera, and their known distributions were incorporated into the model to assess their effect on pest distribution.
3. Suitable regions for ALB are predicted to be widely distributed under both historical and future climate conditions, and across all continents except Antarctica. With climate change, climate suitability would increase in the regions north of 30°N and decline in most regions south of 30°N.
4. The area of most climate-suitable regions would be covered by potential hosts, and optimum hosts would dominate. The possibility of ALB outbreaks in the Northern Hemisphere is much higher than in the Southern Hemisphere, owing to the richer abundance of hosts.
5. These results provide theoretical guidance for developing effective ALB monitoring and mitigation measures.

     

Environmental contamination with Metarhizium anisopliae from fungal bands for control of the Asian longhorned beetle, Anoplophora glabripennis (Coleoptera: Cerambycidae)

Our objective was to determine whether conidia from non-woven fiber bands impregnated with Metarhizium anisopliae F 52 could be spread to other parts of the environment, and whether Anoplophora glabripennis could become infected with conidia dispersed from fungal bands. In the field, bands containing M. anisopliae were hung at 3 m height on 15 trees. Bark samples were taken 10, 20, and 30 cm above the bands and 10, 30, and 60 cm below the bands 2, 5, and 9 days after band placement to quantify conidial densities. There were more conidia in samples taken below bands compared with samples taken above bands. A significant positive correlation was found between rainfall and the occurrence of conidia on any of the bark samples. A laboratory study was conducted to determine whether conidia from M. anisopliae fungal bands could be spread to other parts of the environment by A. glabripennis adults and whether A. glabripennis could become infected by conidia dispersed from fungal bands. One or five adult A. glabripennis were used to contaminate artificial environments with conidia. All adults subsequently exposed to contaminated environments were killed by fungal infection. Beetles exposed to environments that had been contaminated by five beetles died in fewer days compared with environments contaminated by one beetle. Beetles in both density treatments died in fewer days than beetles exposed to environments without M. anisopliae conidia. Our results indicate that environmental contamination with conidia from fungal bands can occur, and that adult A. glabripennis can acquire infection from a contaminated environment.     

Isolation and characterization of microsatellite loci for the Asian longhorned beetle, Anoplophora glabripennis

We describe the first isolation of SSR (simple sequence repeat) markers for Anoplophora glabripennis, a pest of forests in China and urban trees in the USA. Ten markers were developed using FIASCO (fast isolation by AFLP of sequences containing repeats) with an (AC)(17) probe, and five markers were identified in expressed sequence tags found on the NCBI database. Twenty-seven beetles from a population in Gansu Province, China, were assayed. The number of alleles ranged from 3 to 9; observed and expected heterozygosities ranged from 0.07 to 0.79 and from 0.30 to 0.78, respectively.     

History and development of an isolated outbreak of Asian longhorn beetle Anoplophora glabripennis (Coleoptera: Cerambycidae) in southern England

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Timing and duration of the life cycle of Asian longhorn beetle Anoplophora glabripennis (Coleoptera: Cerambycidae) in southern England

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Seasonal changes in supercooling capacity and major cryoprotectants of overwintering Asian longhorned beetle (Anoplophora glabripennis) larvae

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Ecology and management of exotic and endemic Asian longhorned beetle Anoplophora glabripennis

• 1 The Asian longhorned beetle is native to China and Korea, and was found for the first time outside its native habitat in the U.S.A. in 1996, with subsequent detections being made in Canada and several European countries.
• 2 We review the taxonomy, distribution, basic biology, behaviour, ecology and management of endemic and exotic Anoplophora glabripennis, including information that is available in the extensive Chinese literature.
• 3 This species has caused massive mortality of Populus species in China and models have demonstrated that it could become established in many locations worldwide.
• 4 Anoplophora glabripennis is polyphagous but prefers Acer, Salix and Populus, section Aigeiros.
• 5 Although A. glabripennis adults do not disperse far when surrounded by host trees, they have the potential to fly more than 2000 m in a season.
• 6 Volatile organic compounds from preferred host trees are attractive to A. glabripennis and this attraction is heightened by drought stress. Males and females orientate to a volatile released by female A. glabripennis and males attempt to copulate after contacting a sex pheromone on the female cuticle.
• 7 At present, A. glabripennis is being (or has been) eradicated from areas where it has been introduced. After detection, extensive surveys are conducted and, if breeding populations are detected, at the very least, infested trees are removed and destroyed. Close attention is paid to imported solid wood packaging material to prevent new introductions.
• 8 Standard practice to control A. glabripennis in China is to spray insecticides in tree canopies. In North America, largely as a preventative measure, systemic insecticides are injected into trees. Entomopathogenic fungi have been developed for the control of A. glabripennis, and entomopathogenic nematodes, coleopteran and hymenopteran parasitoids and predatory woodpeckers have been investigated as biocontrol agents.
• 9 Ecological control of A. glabripennis in China involves planting mixtures of preferred and nonpreferred tree species, and this practice can successfully prevent outbreaks.

     

大斑啄木鸟对光肩星天牛幼虫捕食的功能反应和数值反应

光肩星天牛Anoplophora glabripennis（Motsch．）是我国重要林木蛀干害虫,造成了巨大的经济损失（张星耀、骆有庆,2003）。大斑啄木鸟Picoides major（L．）是林业蛀干类害虫的重要天敌,关于啄木鸟对蛀干类害虫的控制作用国内已有一些报道,     

光肩星天牛产卵刻槽含水量与pH值的分析

测定了光肩星天牛Anoplophora glabripennis(Motsch.)在柳树皮上产卵刻槽、模拟刻槽及健康树皮的含水量和pH值。结果表明:柳树在不同受伤条件下的含水量及pH值都有所不同,其中含水量的顺序为产卵刻槽>健康树皮>模拟刻槽;pH值的顺序为产卵刻槽>模拟刻槽>健康树皮。这些结果为进一步研究刻槽内微生物的种类和丰度及树木在不同受伤条件下的生理反应提供依据。     

Midgut proteinase activities in larvae of Anoplophora glabripennis (Coleoptera: Cerambycidae) and their interaction with proteinase inhibitors

The major proteinase activities in the larval midgut of a common poplar tree borer, Anoplophora glabripennis, were characterised. Overall digestive capacity, as measured by casein hydrolysis, showed a pH optimum between 10 and 11.5, suggestive of serine endopeptidase activity. Trypsin, chymotrypsin, and chymotrypsin-like activities were detected using specific p-nitroanilide synthetic substrates and by use of specific serine endopeptidase inhibitors. These activities also showed pH optima in the extreme alkaline range. The absence of cysteine, aspartic, and metallo-endopeptidases were confirmed using class specific proteinase inhibitors. The dominant exopeptidase in the midgut is leucine aminopeptidase with a pH optimum of 7–9. Carboxypeptidase a and b activity were barely detectable. A large range of serine endopeptidase inhibitors were screened and were found to vary widely in their ability to inhibit casein hydrolysis. Potato proteinase inhibitor 1 (a chymotrypsin inhibitor) and wheat-germ trypsin inhibitor 1 inhibited particularly effectively in tandem and represent possible candidates for gene transformation to produce plants tolerant to this pest. © 1996 Wiley-Liss, Inc.