No abstract

Roads are an omnipresent feature of the contemporary landscape and are associated with extensive ecological impacts, including habitat degradation, changes in animal behavior, and increases in wildlife mortality. Road ecology has grown into a dynamic multidisciplinary research area within the environmental sciences, aiming to avoid, minimize, and offset the impacts of road use. However, current best practices in mitigation are often incomplete, failing to account for the full suite of environmental problems that roads create and for the causal mechanisms of those problems. We highlight one environmental problem that is largely absent from the road ecology literature – air pollution from motorized vehicles and from road use. Using recent examples, we discuss our current understanding of the ecological effects of air pollution and describe ways to incorporate it into a comprehensive road ecology research framework. Failure to develop such a framework will result in an incomplete representation of the impact that roads have, and will likely diminish the effectiveness of mitigation strategies.

Data accessibility statement Should the manuscript be accepted, data supporting the results will be archived Dryad and the data DOI will be included within the article.

Volatile organic compounds (VOCs) serve as important infochemicals, mediating several ecological interactions including herbivory and pollination. Atmospheric pollutants including traffic‐related air pollution may impair the detection of VOCs used by insects in insect–plant interactions. We investigated the indirect effect of petrol exhaust pollution on olfactory learning and memory (short and long term) in honey bees. Using appetitive olfactory conditioning, we trained bees to learn one of four floral VOC profiles; linalool, dipentene, myrcene and geranium. VOCs were unpolluted or polluted with exhaust collected from a petrol generator. Exhaust emissions included concentrations of CO (246.07 + 17 ppm), NO (20.50 + 6.90 ppb) and NO2 (20.93 + 0.05 ppb) consistent with those typically encountered in urban areas and near roads. Once bees had learnt the training VOC, we tested whether they could recognise that VOC 1 h, 24 h and 48 h post‐training. Bees took significantly longer to learn polluted VOCs and forgot them faster than unpolluted ones. We also tested the ‘masking’ potential of pollution on floral VOCs. Using gas chromatography mass spectroscopy we noted differences in the chemical profile of polluted versus unpolluted VOCs and tested whether bees could recognise polluted VOCs if trained using unpolluted ones. For several VOCs tested, bees could distinguish between polluted and unpolluted VOCs. Ultimately, our results show that air pollution changes the recognition and retention of floral VOCs by bees which may consequently impact foraging efficiency.

Ground-nesting bees are largely undervalued, both in terms of their use as model species for behavioural studies, and in terms of their agricultural benefit as pollinators in crop systems. But, why? One potential barrier limiting their use as model species may be our understanding of how to effectively establish and maintain groundnesting bees in the laboratory. Here we review how artificial nests are used to study ground-nesting bees and provide guidelines for building, starting and maintaining artificial nests. Ultimately, appropriate design and maintenance of artificial nests will allow researchers to explore a suite of interesting questions related to this important group of pollinating insects, from natural history to the origins of eusociality and the effects of environmental contaminants. ground-nesting bee / artificial nest / rearing / Lasioglossum

Changes in the mean and variance of phenotypic traits like wing and head morphology are frequently used as indicators of environmental stress experienced during development and may serve as a convenient index of urbanization exposure. To test this claim, we collected adult western honey bee (Apis mellifera Linnaeus 1758, Hymenoptera, Apidae) workers from colonies located across an urbanization gradient, and quantified associations between the symmetries of both wing size and wing shape, and several landscape traits associated with urbanization. Landscape traits were assessed at two spatial scales (three km and 500 m) and included vegetation and anthropogenic land cover, total road length, road proximity and, population and dwelling density. We then used geometric morphometric techniques to determine two wing asymmetry scores—centroid size, a measure of wing size asymmetry and Procrustes distance, a measure of wing shape asymmetry. We found colony dependent differences in both wing size and shape asymmetry. Additionally, we found a negative association between wing shape asymmetry and road proximity at the three km buffer, and associations between wing shape asymmetry and road proximity, anthropogenic land cover and vegetation cover at the 500 m buffer. Whilst we were unable to account for additional variables that may influence asymmetry including temperature, pesticide presence, and parasitism our results demonstrate the potential usefulness of wing shape asymmetry for assessing the impact of certain landscape traits associated with urbanization. Furthermore, they highlight important spatial scale considerations that warrant investigation in future phenotypic studies assessing urbanization impact.

Wind is a pervasive environmental stress that may directly alter the behaviour of insect herbivores, thus limiting the ability to find and assimilate food and avoid natural enemies. We investigated the direct effects of wind on larvae of gum leaf skeletoniser Uraba lugens Walker by investigating their movement patterns and plant micro‐site selection. We allocated individuals to Eucalyptus tereticornis plants and exposed them to zero (control) or moderate wind speeds (3 m/s) for 2 h and quantified their movement patterns. When exposed to wind, individuals dropped from plants, and a greater proportion of individuals were found on petioles, branches, the underside of leaves and the leeward side of plants. The dramatic effects of wind on larval behaviour, even at relatively moderate intensities, reveal the significant potential of wind to influence plant–insect interactions.

Coalmines, which are major contributors of particulate matter in the form of coal dust, are expanding globally into rural environments. However, ecological effects on organisms interacting with coal‐dusted foliage in mining landscapes are unknown. We tested how the behaviour, development and survival of a polyphageous insect herbivore, Helicoverpa armigera (Hübner) (Lepidoptera: Noctuidae) is affected by consuming tomato leaves Lycopersicon esculentum laden with coal dust. We tested (a) feeding site establishment preference of neonates, (b) feeding behaviour and leaf consumption of late‐instar larvae, (c) survival of neonates and (d) survival and development of late‐instar larvae. We found that coal dust consumption increased the mortality of late‐instar larvae but did not influence their development. Despite long‐term implications for survival, late‐instar larvae did not adjust their feeding behaviour or the amount of leaf material consumed in response to foliar coal dust. Contrastingly, when neonate H. armigera were given a choice, they avoided establishing themselves on the coal‐dusted adaxial surface of leaves. Neonate mortality was 99% within 7 days, with no effect of coal dust. Our study provides the first data on the impact of coal dust on an insect herbivore. This has implications for ecological interactions in landscapes adjoining coalmines.