The effects of insecticide dose and herbivore density on tri-trophic effects of thiamethoxam in a system involving wheat, aphids, and ladybeetles
Introduction
Since their introduction in 1991, neonicotinoid insecticides have become commonly used in many agricultural settings to control pest insects (Nauen and Denholm, 2005). Neonicotinoids act as agonists to the acetylcholine receptors within the nervous system of an animal, mimicking the action of naturally produced acetylcholine (Jeschke et al., 2013), a neurotransmitter which allows action potentials to move from nerve cell to nerve cell. The overstimulation of nerve cells due to neonicotinoid insecticides can cause paralysis (Girolami et al., 2009) and death (Iwasa et al., 2004) in insects. The popularity of neonicotinoid use has risen in part because of the diverse means by which the chemicals can be applied. This class of insecticides can be applied as granules in the soil (Lanka et al., 2014), foliar sprays (Juraske et al., 2009), soil drenches (Stoner and Eitzer, 2012), tree injections (Cowles et al., 2006) and topically to animals (Dryden et al., 2011). However, the most widespread application method of neonicotinoids has been as seed treatments that protect plants from herbivory (Jeschke et al., 2010).
Although the threat against beneficial insects is reduced by using systemic insecticides compared to broad spectrum insecticidal sprays, there is evidence that systemically treated plants do in fact harm beneficial insects through a number of pathways (Lundgren, 2009). For example, Moser and Obrycki (2009) exposed Asian ladybeetle (Harmonia axyridis Pallas (Coleoptera: Coccinellidae)) larvae to corn seedlings grown from seed treated with neonicotinoids. The ladybeetle larvae expressed neurotoxic symptoms such as trembling, paralysis and loss of coordination in 72% of cases, presumably the result of the observed and quantified facultative herbivory (Moser and Obrycki, 2009). In another toxicology study, Rogers et al. (2007) confined Chrysoperla carnea (Neuroptera: Chrysopidae) adults to the flowers of neonicotinoid treated Fagopyrum esculentum and Asclepias curassavica where they consumed the nectar. Survival of C. carnea was significantly reduced in the insecticide treatment after 10 d compared to an untreated control group; the authors concluded that survival was diminished due to the ingestion of nectar containing neonicotinoid insecticide (Rogers et al., 2007).
Besides direct mortality of beneficial insects resulting from the use of systemic neonicotinoids, sub-lethal concentrations of insecticide within plants can act as one of a suite of stressors that result in diminished fitness of non-target species. Consequences of ingesting sub-lethal concentrations of insecticides can include reduced fecundity (Shi et al., 2011), lowered mobility (Scholer and Krischik, 2014), loss of orientation abilities (Fischer et al., 2014), limited overwintering survivability (Grewal et al., 2001) and reduced foraging capacity (Schneider et al., 2012). The sub-lethal effects of neonicotinoids can potentially reduce the efficiency of predator and parasitoid communities, threatening biotic resistance to pest proliferation (Seagraves and Lundgren, 2012).
Predation on crop pests by predators and parasitoids provides not only environmental benefits, but also has tangible economic value to land owners, and is an important component of Integrated Pest Management (IPM) (Zhang and Swinton, 2009). Plant incorporated systemic insecticides may affect non-target predators through various trophic pathways, primarily considered bi-trophic (Lundgren, 2009), or tri-trophic (prey-mediated) effects (Birch et al., 1999). Beneficial insects are exposed to systemic insecticides through omnivory on non-prey foods such as vegetative plant tissue (Moser and Obrycki, 2009), pollen (Cresswell, 2011, Dively and Kamel, 2012), guttation fluid (Girolami et al., 2009), floral (Krischik et al., 2007) or extra-floral nectar (Stapel et al., 2000). Predators can also be adversely affected by an insecticide if their herbivorous prey contains the toxin or the quality of the prey is lessened by ingesting insecticide-containing plant tissues (Dutton et al., 2002). Documenting the trophic relationships between systemically treated-plants, pests and beneficial insects is important for understanding the compatibility of systemic insecticides within IPM systems.
Wheat is a crop of significant importance worldwide; 18.5 million ha of wheat was harvested in the United States in 2013 alone (NASS, 2014). Rhopalosiphum padi (L.) (bird cherry-oat aphid, Hemiptera: Aphididae) is a common pest of wheat in the U.S. and worldwide, causing significant damage resulting from feeding and transmitting viruses (Jiménez-Martínez et al., 2004). Neonicotinoid seed treatments are highly water soluble (Maienfisch et al., 2001) and are readily transported through both xylem and phloem, making this class of insecticides and method of application well adapted for the control of phloem feeding insects, like aphids (Magalhaes et al., 2009), in a variety of crops including wheat (Gray et al., 1996).
Members of the Coccinellidae family have historically been used frequently and effectively as a useful tool in biological control programs to limit pest arthropod herbivory (Biddinger et al., 2009, Weber and Lundgren, 2009), especially from aphids (Obrycki et al., 2009). One species of Coccinellidae, Coleomegilla maculata DeGeer (Coleoptera: Coccinellidae), is a predator of R. padi in wheat (Elliott et al., 1999) and in other crops including corn (Lundgren and Wiedenmann, 2005), thus C. maculata could potentially be affected tri-trophically by aphids feeding on systemically treated wheat. Sublethal levels of neonicotinoid insecticides can be found in crops either as the seed treatment dissipates over the season (McCornack and Ragsdale, 2006, Seagraves and Lundgren, 2012), or through uptake of residual insecticides found in the soil from previous insecticide applications. Here we examine the tri-trophic interactions among wheat plants containing sublethal doses of thiamethoxam, aphids, and the predatory C. maculata. Specifically, we examined how insecticide dose in the wheat plants and aphid densities on the wheat plants interact to affect C. maculata larvae.
Section snippets
Insects and plants
A C. maculata DeGeer colony was established from individuals collected from a corn field near Brookings, SD, USA (44.3114° N, 96.7981° W), and was raised for three generations (approximately 15 mo) in the laboratory. The colony was maintained on a semi-artificial diet (Lundgren's Super C. mac Diet, (Lundgren et al., 2011)) and honey. The beetles were raised at 26.5 °C with 16:8 h (L:D; light: dark) photoperiod. The R. padi colony was established from individuals collected in Hays, Kansas.
Effect of thiamethoxam dose and aphid density on toxin levels in plant and prey
The concentration of thiamethoxam in the soil drenches were positively correlated with the thiamethoxam concentration found in wheat tissue (Fig. 1A). The level of aphid infestation on wheat plants significantly (P = 0.03) affected how much thiamethoxam was detected within wheat tissue (Fig. 1B). In particular, wheat that had five aphids per plant had significantly more thiamethoxam than treatments that had greater aphid infestations. Thiamethoxam was undetectable in aphids, but clothianidin
Discussion
Our study revealed that herbivore density interacts with systemic neonicotinoid insecticides in ways that may affect higher trophic levels responsible for regulating pest insect populations. Aphids fed wheat treated with sub-lethal doses of thiamethoxam had a measurable adverse, prey-mediated effects on the fitness of young lady beetle larvae, but only when aphids were less crowded on the plants. Aphid density had an effect on the amount of insecticide detectable within the plants as well.
Acknowledgments
The authors would like to thank Janet Fergen, Ryan Schmid, Megan Wentzel and Mallory Wentzel for assistance in the laboratory. Helpful advice was given by Frank Byrne in synthesizing an ELISA protocol. Mention of proprietary products does not constitute endorsement by the USDA.
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