大气臭氧浓度升高对银杏叶片活性氧代谢及相关基因表达的影响

采用开顶式气室熏蒸法,设置自然条件下臭氧(O₃)浓度(对照,约40 nmol·mol^-1)、80、160及200 nmol·mol^-14个臭氧浓度,观测了不同浓度臭氧条件下银杏叶片可见伤害、活性氧生成量、抗氧化酶活性及相关基因表达变化情况,分析大气臭氧浓度升高对植物活性氧代谢的影响.结果表明: 160和200 nmol·mol^-1 O₃熏蒸明显伤害银杏叶片,80 nmol·mol^-1与对照无差异,无可见伤害.O₃处理20 d后,160和200 nmol·mol^-1条件下银杏叶片的超氧自由基(O₂^-·)产生速率显著高于80 nmol·mol^-1和对照,而80 nmol·mol^-1与对照无差异;O₃处理40 d后,160和200 nmol·mol^-1熏蒸下叶片过氧化氢(H₂O₂)含量显著高于80 nmol·mol^-1和对照,而过氧化氢酶(CAT)活性显著高于80 nmol·mol^-1和对照,各臭氧处理抗坏血酸过氧化物酶(APX)活性均低于对照.熏蒸40 d后,CAT、APX基因的转录表达持续加强;防御素(GbD)的表达强度则随着臭氧浓度的增加及熏蒸时间的延长而呈显著加强.高浓度臭氧胁迫可使银杏叶片活性氧生成量增加、抗氧化酶活性下降、相关基因表达水平上调,有明显可见叶片伤害.     

植物的臭氧污染胁迫效应研究进展

近地面空气中的臭氧(O₃)属于二次污染物,是由氮氧化物(NO_x)和挥发性有机物(VOCs)等前体物在一定的环境条件下形成的。近年来,全球受O₃污染的区域增加,污染程度也日趋严重。O₃污染对植物的危害引起了国内外研究人员的广泛关注。众多研究发现,不同植物对O₃的敏感性不同,其大小主要取决于植物自身的特性及环境因素;O₃污染降低植物的净同化作用,减缓植物生长,改变同化物的分配,可对物种间的相互关系以及生态系统结构产生深远影响。该文在综述了国内外研究进展的基础上,提出我国在O₃污染研究领域应深入研究以下几个方面:1)选育具有对O₃污染抗性较强的植物尤其是作物品种;2)深入研究减轻O₃污染对植物危害的栽培管理措施;3)加强研究O₃污染对我国自然生态系统的影响;4)研究植被在治理O₃污染中的积极作用。     

地表臭氧浓度升高与干旱交互作用对杨树非结构性碳水化合物积累和叶根分配的短期影响

人类活动加剧和全球变化导致植物在生长季同时受到高浓度地表臭氧(O₃)和干旱的双重胁迫。为了探究两者对植物非结构性碳水化合物(TNC)积累和分配的影响, 该实验采用开顶式气室研究了2种O₃浓度(CF, 过滤空气; NF40, NF (未过滤空气) + 40 nmol·mol ^-1 O₃)和2个水分处理(对照, 充分灌溉; 干旱, 非充分灌溉)及其交互作用对杨树基因型‘546’ (Populus deltoides cv. ‘55/56’ × P. deltoides cv. ‘Imperial’)叶片和细根中TNC及其组分(葡萄糖、果糖、蔗糖、多糖、总可溶性糖和淀粉)含量的影响。结果表明: O₃浓度升高显著降低杨树叶片中淀粉和TNC的含量, 增加葡萄糖、果糖和总可溶性糖含量, 但对细根中淀粉和总可溶性糖含量的影响不显著。干旱胁迫显著增加细根中果糖和多糖含量, 降低蔗糖含量, 但对叶片中淀粉和总可溶性糖含量的影响不显著。充分灌溉下O₃浓度升高显著增加了杨树叶片多糖和总可溶性糖含量, 而干旱下O₃浓度升高显著增加了TNC含量的根叶比。该研究结果发现O₃主要影响叶片中TNC及各组分的含量, 而干旱主要影响细根中TNC及各组分的含量。从杨树叶片TNC的响应来看, 适度的水分限制有助于减缓O₃的负面伤害。     

地表臭氧浓度升高对陆地生态系统影响的研究进展

浓度不断升高的地表臭氧(O₃)已成为全球性环境问题, 中国也不例外。目前, 高浓度O₃对叶片光合气体交换、植物生长或生物量的影响已备受关注, 但有关O₃对生态系统层次的研究还相对稀缺且存在较大的不确定性。该文梳理了近40年来地表O₃浓度及其影响相关领域的发展趋势和研究热点, 回顾了地表O₃浓度升高对植物影响的研究手段和评估方法, 综述了地表O₃浓度升高对陆地生态系统影响方面取得的重要进展, 主要包括植物应对O₃胁迫的响应机制、地表O₃对粮食产量和作物品质、生态系统固碳能力、群落结构和地下过程的影响及地表O₃污染区域风险; 此外, 针对目前研究的不足, 对未来研究进行了展望。建议利用先进的完全开放式O₃熏蒸系统模拟O₃浓度升高对生态系统影响的同时加强对地下生态过程的研究, 开展O₃与其他环境因子的复合作用研究; 关注O₃污染对粮食安全的影响; 开展联网研究, 建立统一评价体系; 探索减缓地表O₃污染的生态防控措施; 以期为地表O₃污染生态效应领域的发展提供助力。     

Progress in the effects of elevated ground-level ozone on terrestrial ecosystems

浓度不断升高的地表臭氧(O₃)已成为全球性环境问题, 中国也不例外。目前, 高浓度O₃对叶片光合气体交换、植物生长或生物量的影响已备受关注, 但有关O₃对生态系统层次的研究还相对稀缺且存在较大的不确定性。该文梳理了近40年来地表O₃浓度及其影响相关领域的发展趋势和研究热点, 回顾了地表O₃浓度升高对植物影响的研究手段和评估方法, 综述了地表O₃浓度升高对陆地生态系统影响方面取得的重要进展, 主要包括植物应对O₃胁迫的响应机制、地表O₃对粮食产量和作物品质、生态系统固碳能力、群落结构和地下过程的影响及地表O₃污染区域风险; 此外, 针对目前研究的不足, 对未来研究进行了展望。建议利用先进的完全开放式O₃熏蒸系统模拟O₃浓度升高对生态系统影响的同时加强对地下生态过程的研究, 开展O₃与其他环境因子的复合作用研究; 关注O₃污染对粮食安全的影响; 开展联网研究, 建立统一评价体系; 探索减缓地表O₃污染的生态防控措施; 以期为地表O₃污染生态效应领域的发展提供助力。     

臭氧浓度升高对坪用高羊茅生长、亚细胞结构及活性氧代谢的影响

通过开顶箱(OTCs)模拟,以环境臭氧(O₃)浓度约40 nmol·mol^-1为对照,研究大气O₃浓度升高(80和160 nmol·mol^-1O₃)对冷季型草坪草高羊茅生长、亚细胞结构及其活性氧代谢的影响.结果表明: 14 d的80 nmol·mol^-1O₃熏蒸使高羊茅株高和叶宽降低,总生物量降低43.7%,老叶变黄,而160 nmol·mol^-1O₃处理高羊茅叶出现大量枯死褐斑,叶尖坏死,新叶卷曲,总生物量降低46.2%,叶肉细胞膜卷曲,叶绿体和线粒体受损严重.与对照相比,80和160 nmol·mol^-1O₃熏蒸下高羊茅叶片超氧阴离子(O₂^-·)产生速率、过氧化氢(H₂O₂)和丙二醛(MDA)含量显著增加,抗氧化酶活性显著升高,但叶片总酚含量和抗氧化能力随O₃浓度升高而先升高后降低.在明显O₃伤害症状出现之前,O₃已对高羊茅的生长和抗氧化代谢产生不利影响;高羊茅抗氧化系统虽对O₃浓度的升高存在一定的适应性反应,但其不能抵御过高浓度的长期胁迫和伤害.     

二氧化硫对墨西哥豆瓢虫的影响

空气污染对害虫的影响,国内尚无研究报道。本文报道了作者在美国农业研究中心植物胁迫实验室进行的部分工作。实验结果表明,在0.30ppmSO_2的作用下,墨西哥豆瓢虫(Epilachna varivestis)的取食量和蛹重增加;与未受污染的寄主植物相比,豆瓢虫偏食受污染的植物;而且有嗜食含较高糖分寄主植物的倾向;在污染空气中长成的成虫可消耗更多的植物物质。     

Effects of elevated ozone and nitrogen addition on leaf nitrogen metabolism in poplar

臭氧和氮添加对杨树叶片氮代谢的影响 臭氧(O₃)污染和氮(N)沉降/施肥都能同时影响植物的生长。然而，几乎没有研究探究O₃和N添加对植物叶片N代谢过程的复合影响。本研究在开顶式气室(OTC)中对杨树进行了为期95 d的熏蒸实验，包括两个O₃水平(NF，环境O₃水平；NF60，NF + 60 ppb O₃)和4个N处理(N0，没有N添加；N50，N0 + 50 kg N ha⁻¹ yr⁻¹；N100，N0 + 100 kg N ha⁻¹ yr⁻¹；N200，N0 + 200 kg N ha⁻¹ yr⁻¹)。测定了与叶片N代谢相关的一些指标，包括叶片N代谢酶的活性、总叶片N浓度、NO₃⁻-N浓度、NH₄⁺-N浓度、总氨基酸浓度(TAA)、总可溶性糖的浓度(TSP)。研究结果表明，相对于NF，在8月份NF60处理显著刺激了硝酸还原酶(NR)的活性，使其升高了47.2%。当平均所有的N处理和两次取样时间时，NF60处理下谷氨酰胺酶(GS)的活性比NF处理下的高57.3%。但是O₃处理并没有显著影响TSP浓度，并且在8月也没有降低TAA的浓度。相对N0，高的N添加处理(N200)显著增加了杨树叶片的饱和光合速率(A_sat) 24%，并且分 别在8和9月增加了总叶片N浓度70.3%和43.3%。但是在8月份，N200处理下光合N利用效率比N0的低26.1%。这表明N添加导致的A_sat和叶片总的N浓度的升高是不匹配的，高N处理下，叶片中一些剩余的N没有被用于优化植物碳的同化。同时，也发现高N添加显著刺激了叶片N代谢过程，叶片中的NO₃⁻-N浓度、NH₄⁺-N浓度、TAA浓度、NR和GS活性都显著升高。然而，O₃和N添加对杨树叶片所有N代谢相关的指标都没有交互影响。这些结果将有助于更好地了解在高O₃污染和N沉降/施肥下植物的N代谢过程以及生物地球化学循环过程。     

城市植物挥发性有机化合物排放与臭氧相互作用及其机制

近地面臭氧(O₃)已成为继PM_2.5后影响我国空气质量的一种重要二次污染物。随着氮氧化物浓度的持续下降和气候变暖的加剧,城市O₃的形成对挥发性有机化合物的浓度更加敏感。近年来城市绿色空间显著增长,植物源挥发性有机化合物(BVOCs)排放和浓度逐年增加。针对BVOCs与近地面O₃之间复杂的交互作用,从植物BVOCs的特性与作用出发,综述了不同因素尤其是O₃浓度增加对树木生理状态及BVOCs排放速率的影响,定量分析了已有研究中O₃对不同植物异戊二烯和单萜烯排放速率的影响,以及BVOCs对O₃形成的贡献,总结了BVOCs与O₃相互作用研究领域存在的不足。未来亟需加强的研究包括：(1)城市树种BVOCs排放因子的实测,建立物种的排放速率数据库,优化模型参数,提升精细尺度BVOCs排放量估算模型精度;(2)多种环境因子,比如污染物浓度、温湿度等对城市植物BVOCs排放的交互作用和综合影响的研究;(3)植物BVOCs对O     

高浓度二氧化碳和臭氧对蒙古栎叶片活性氧代谢的影响

利用开顶箱熏蒸法,研究了高浓度O₃(≈80 nmol·mol^-1)和高浓度CO₂(≈700 μmol·mol^-1)及其复合处理对蒙古栎叶片活性氧代谢的影响.结果表明：高浓度O₃显著增加了蒙古栎叶片超氧阴离子(O₂^•)产生速率、过氧化氢(H₂O₂)和丙二醛(MDA)含量和电解质外渗率(P<0.05),显著降低了超氧化物歧化酶(SOD)、过氧化氢酶(CAT)、抗坏血酸过氧化物酶(APX)活性和抗坏血酸(AsA)含量(P<0.05).高浓度CO₂对蒙古栎叶片活性氧代谢影响不显著.高浓度O₃和CO₂复合处理的叶片O₂^•产生速率、H₂O₂和MDA含量和电解质外渗率上升不明显,说明高浓度CO₂缓解了高浓度O₃对蒙古栎叶片的氧化胁迫.复合处理的叶片SOD、CAT、APX活性以及AsA和总酚含量显著高于O₃处理的叶片(P<0.05),说明高浓度CO₂缓解了高浓度O₃对叶片抗氧化系统的消极影响.     

Growth compensation and faster development of Colorado potato beetle (Coleoptera: Chrysomelidae) feeding on potato foliage expressing oryzacystatin I

Feeding, growth, development, and food conversion efficiency of Colorado potato beetle larvae reared on foliage from a “Kennebec” potato line expressing oryzacystatin I (OCI) at about 1% of its total soluble proteins were compared to those of larvae feeding on untransformed foliage from the same line. During stages L1 to L3, larvae feeding on OCI consumed leaf material 14% faster, gained weight 28% faster, and weighed 20% more at the end of the L3 stage, compared to controls. Continued exceptional performance on OCI during the final L4 stage was expressed as faster development than controls, an effect that persisted during pupal development and resulted in emergence of similar weight adults 1 day earlier than controls. Larvae initially maintained on control foliage and switched to OCI foliage during L4 did not overcompensate as those on OCI foliage throughout development, but performed similarly to larvae on control foliage throughout. Total azocaseinase activity in midgut extracts from these 4th instars 1 d after switching to OCI foliage was sensitive to inhibition by a recombinant form of OCI expressed in Escherichia coli, but was no longer sensitive 4 d after switching, indicating a gradual adaptation of the insect digestive protease system, based on the production of OCI insensitive proteases. Despite OCI potato foliage being consumed faster by small larvae using it for food, there was no indication that it was less efficient than untransformed foliage as food protein. Arch. Insect Biochem. Physiol. 40:69–79, 1999. © 1999 Wiley‐Liss, Inc.     

Impact of balsam fir flowering on pollen and foliage biochemistry in relation to spruce budworm growth, development and food utilization

The impact of balsam fir (Abies balsamea (L.) Miller) flowering on nutritional and allelochemical quality of pollen, current-year and one-year-old foliage is studied in relation to spruce budworm (Choristoneura fumiferana Clem.) (Lepidoptera: Tortricidae) growth, development and utilization of food and nitrogen. In the laboratory, using fresh food from the field, we simulated conditions of low larval population density, in which there is no current-year foliage depletion during the spruce budworm feeding period. Similarly, we simulated conditions of high larval population density when current-year foliage depletion occurs.Because of the high nutritive value of pollen (high amounts of amino acids and minerals, especially nitrogen; low monoterpene content), insects from flowering trees reached the fifth instar five days earlier than those from non-flowering trees, and had heavier dry- and nitrogen-weights at the beginning of the fifth instar. At budbreak, switching from pollen to current-year foliage negatively affected conversion efficiencies and digestibilities of food and nitrogen (AD; ADN; ECDN; ECI; ECIN). The switch from pollen to new foliage had a detrimental impact on fifth-instar survival and on newly-moulted sixth-instar dry- and nitrogen-weights. Moreover, during the fifth instar, balsam fir flowering reduced the nutritive value of current-year foliage, which in turn, might have contributed to the reduced larval growth. Nevertheless, during the sixth instar, balsam fir flowering affected the biochemistry of current-year foliage in ways that enabled larvae to compensate for their low fifth-instar biological performance; larvae also managed to reach pupal dry weight similar to larvae reared on non-flowering trees. Current-year foliage from flowering trees contained less nitrogen, total soluble sugars and total monoterpenes. Those foliar characteristics enabled larvae to increase food and nitrogen consumption rates (RCR; RNCR), because of lower repellency and/or post-ingestional feedback from monoterpenes.As for current-year foliage, balsam fir flowering reduced nitrogen, total soluble sugar and total monoterpene contents in one-year-old foliage during the sixth-instar feeding period. These characteristics enabled sixth-instar larvae, fed on old foliage from flowering trees, to have high relative food and nitrogen consumption rates (RCR; RNCR). Larvae were also able to reach higher relative growth rates (RGR) and relative nitrogen accumulation rates (RNAR) compared to larvae reared on one-year-old foliage from non-flowering trees. Finally, larvae on flowering trees had pupal dry weight similar to those from non-flowering trees, but reached the adult stage nine days earlier.Regardless the foliage type consumed by spruce budworm larvae during the sixth instar, pollen consumption during early larval stages reduced total development time, and thus exposure time to natural enemies. This phenomenon might increase larval survival. Balsam fir flowering changed the biochemistry of one-year-old and current-year foliages, but did not affect pupal dry weights of larvae reared on flowering trees compared to those reared on non-flowering trees. Thus, at low population density, spruce budworm populations in balsam fir flowering stands might be favoured over those in balsam fir non-flowering stands. In addition, when larvae consumed one-year-old foliage during the entire sixth instar, those on flowering trees are probably favoured over those on non-flowering trees. However, because flowering trees produce less new foliage than non-flowering trees, current-year foliage depletion may occur earlier on flowering trees than on non-flowering trees. Thus, at similar larval population density, larvae on flowering trees might have to feed on one-year-old foliage earlier than those on non-flowering trees. In that case, spruce budworm populations on non-flowering stands would be favoured over those on flowering stands.     

Genetic transformation of potato with nptII-gus marker genes enhances foliage consumption by Colorado potato beetle larvae

Little is known about the effect of transgenic plants containing commonly used marker genes, such as aph(3)II (nptII encoding neomycinphosphotransferase) and uidA (gus encoding -glucuronidase) on insect feeding behaviour. We report here, for the first time, that transgenic potato plants containing only nptII and gus marker genes enhance foliage consumption by the Colorado potato beetle (CPB, Leptinotarsa decemlineata S.). Transformation of potato cultivar Désirée was performed with Agrobacterium tumefaciens. Internode explants were inoculated with different strains of bacteria, carrying either nptII-gus or nptII alone. A total of 180 transgenic and untransformed control plants were grown in the greenhouse for the analysis of food consumption by CPB. For each transformed and untransformed line tested, four bioassays were conducted each consisting of 10 second-instar larvae feeding independently on a 2 cm diameter leaf disc for 20 h. Our data show up to 50% increase of mean foliage consumption on plants transformed with the nptII-gus construct, indicating that transgenic plants containing these marker genes can affect the feeding behaviour of the insects. These results were obtained from the primary regenerants (R₀ lines) as well as from tuber-derived plants (R₁ lines). Further tests with transgenic plants containing the nptII marker gene only, showed no significant difference in feeding when compared to untransformed control plants, allowing us to rule out a direct effect of this marker gene on foliage consumption by the insect larvae. It is suggested that gus protein is involved in the increase of foliage consumption by CPB.     

The effect of ozone fumigation and different Brassica rapa lines on the feeding behaviour of Pieris brassicae larvae

Elevated levels of tropospheric ozone and their effects on plants have been studied for a great number of years. Ozone is a gaseous pollutant and acts as a phytotoxin. Even though ozone is known to change the physiology of plants, little attention has been given to the indirect effects of ozone on plant-insect interactions. This paper addresses this question by investigating the interactive effects of ozone and plant genotype on insects. Lines of rapid-cycling Brassica rapa (L.) selected for their contrasting sensitivity to ozone and Pieris brassicae (L.) (Lepidoptera: Pieridae) were used as a model system. The effect of differences in ozone sensitivity and ozone fumigation on the plant's carbon and nitrogen pools, the feeding preference, and behaviour of P. brassicae larvae were investigated. The results show that the plant's susceptibility to ozone interacts in a complex way with ozone induced alterations in the suitability of the plant for the insect. Only the larval performance on the sensitive line was affected by ozone exposure. Biochemical changes in the resistant B. rapa line made the plant a better food source for the insects, since the digestibility of this plant was significantly higher than that of the sensitive line, and the larvae pupated more quickly and were heavier.     

Red foliage color reliably indicates low host quality and increased metabolic load for development of an herbivorous insect

Plant chemical defense and coevolved detoxification mechanisms in specialized herbivorous insects are fundamental in determining many insect–plant interactions. For example, Brassicale plants protect themselves from herbivory by producing glucosinolates, but these secondary metabolites are effectively detoxified by larvae of Pierid butterflies. Nevertheless, not all Brassicales are equally preferred by these specialist herbivores. Female Pieris butterflies avoid laying eggs on anthocyanin-rich red foliage, suggesting red color is a visual cue affecting oviposition behavior. In this study, we reared P. brassicae larvae on green and red cabbage leaves, to determine whether foliage color reliably indicates host plant quality. We did not find a difference in survival rates or maximal larval body mass in the two food treatments. However, larvae feeding on red cabbage leaves exhibited significantly lower growth rates and longer durations of larval development. Interestingly, this longer development was coupled with a higher consumption rate of dry food matter. The lower ratio of body mass gain to food consumption in larvae feeding on red cabbage leaves was coupled with significantly higher (ca. 10 %) larval metabolic rates. This suggests that development on red foliage may incur an increased metabolic load associated with detoxification of secondary plant metabolites. Energy and oxygen allocation to detoxification could come at the expense of growth and thus compromise larval fitness as a result of extended development. From an evolutionary perspective, red foliage color may serve as an honest defensive cue, as it reliably indicates the plant’s low quality as a substrate for larval development.     

Factors affecting oral regurgitation by larval spruce budworm

This study evaluated factors that influence the regurgitation behaviour of sixth instar spruce budworm, Choristoneura fumiferana Clemens (Lepidoptera: Tortricidae), reared on balsam fir, Abies balsamea (L.) Mill. (Pinaceae), under various experimental conditions in the laboratory. Upon physical disturbance, larvae discharged a median volume of regurgitant of 0.4 μl when fed and 1.6 μl when food‐deprived. Larvae deprived of food for 24 or 48 h disgorged more regurgitant than larvae feeding on balsam fir foliage, and the effect was consistent for laboratory‐reared and field‐collected larvae. The water content of the foliage fed upon by larvae had no immediate impact on the volume of regurgitant; following a 24‐h period of food deprivation, however, larvae that previously fed on fresh foliage discharged >2.5 times more regurgitant than larvae that previously fed on dry foliage. Self‐regulated regurgitation by larvae, measured using the number of regurgitant stains on filter paper, was >10 times higher when larvae had access to balsam fir foliage than when they were starved. The number of larvae confined inside the Petri dish (one or four individuals) had a relatively small effect on regurgitation. Larvae were deterred from feeding when balsam fir needles were entirely covered with regurgitant, but not when only a portion of the foliage was treated. These results suggest that the regurgitant does not serve as resource marking or spacing pheromone. The high level of regurgitation by larvae after contact with ants suggests that the regurgitant has evolved in part as a defence mechanism against natural enemies.     

What physiological processes permit insects to eat Eucalyptus leaves?

Many species of insects eat Eucalyptus foliage despite its relatively low nutritional value and the many plant secondary metabolites (PSMs) present, for example, terpenes, phenols and formylated phloroglucinols (FPGs). Formylated phloroglucinols are a new class of PSMs that act as antifeedants for possums and koalas. What physiological processes are present that permit insects to eat eucalypt foliage and how do PSMs influence insect feeding or digestion? Some trees seem to be repeatedly infested with eucalypt‐feeding insects, possibly as a result of previous chemosensory cues remaining from parental selection of a plant. Avoidance or storage of PSMs permit jarrah leafminers (Perthida glyphopa) and sawflies (Perga sp.) to consume eucalypt foliage without dealing with the majority of these compounds. Some PSMs can be metabolized by polysubstrate membrane oxidases as found in caterpillars or sawflies that feed on eucalypts. High midgut pH may be advantageous for nutrient extraction and PSM metabolism, and midgut pH ranges between 8.5 and 8.9 for caterpillars of Hyalarcta huebneri. Plant secondary metabolites may not be absorbed as a result of the combined presence of the peritrophic matrix and endogenous surfactants. Excretion of PSMs can be as metabolites or intact compounds. Both putative metabolites and sideroxylonal‐A, an FPG, are present in the faeces of larvae of the case moth, H. huebneri. The presence of sideroxylonal‐A in the food had an effect on the presence of 5‐hydroxytryptamine (5HT) in the central nervous system of caterpillars, as larvae fed leaves with a high concentration of sideroxylonal‐A had relatively more 5HT in the brain and central nervous system ganglia than larvae fed leaves containing a low concentration. Further work is necessary to clarify how PSMs are handled by eucalypt‐feeding insects and what effect FPGs have on feeding and digestion.     

Plant stress and insect performance: cottonwood,ozone and a leaf beetle

Summary Leaf area consumption rates, development rates, survivorship, and fecundity of the imported willow leaf beetle (Plagiodera versicolora Laich) were examined on two clones of eastern cottonwood which were previously exposed to ozone or charcoal-filtered air. P. versicolora consumed more ozone treated foliage, but were more fecund when reared on charcoal-filtered air treated plants. Beetle development rates and survivorship were not significantly different on treated and control cottonwoods. We concluded that: 1) Ozone fumigation of cottonwood reduced foliage quality, and the reproductive success and overall performance of P. versicolora. 2) increased foliage consumption by beetles was probably a mechanism compensating for decreases in foliage quality. 3) Reductions in beetle fecundity were due to an initial reduction in oviposition rates. 4) Beetle feeding preference did not correlate with the suitability of foliage for beetle performance. These results are discussed in relation to the impact of air pollution on plant-insect interactions.