Abstract

Urban environments frequently play an important role in the initial stages of biological invasions, often serving as gateways for non-native species, which may propagate to nearby natural and agricultural ecosystems in the event of spillover. In California, citrus trees are a dominant ornamental and food plant in urban and peri-urban environments. We studied the invasion dynamics of the Asian citrus psyllid (Diaphorina citri), which became widespread in urban areas of southern California starting in 2008, to understand the factors driving its more recent invasion in commercial citrus groves. Using a multi-year monitoring database, we applied a suite of models to evaluate the rate at which groves accrued their first D. citri detection and the cumulative number of detections thereafter. Grove characteristics and landscape context proved to be important, with generally higher invasion rates and more cumulative detections in groves that were larger, had more edge, or had more perforated shapes, with greater urbanization intensity favoring more rapid invasion, but with inconsistent effects of distance to roads among models. Notably, distance to urban or other grove occurrences proved to be among the most important variables. During the early phase of D. citri invasion in the region, groves closer to urban occurrences were invaded more rapidly, whereas more recently, invasion rate depended primarily on proximity to grove occurrences. Yet, proximity to urban and grove occurrences contributed positively to cumulative D. citri detections, suggesting a continued influx from both sources. These results suggest that inherent features of agroecosystems and spatial coupling with urban ecosystems can be important, temporally dynamic, drivers of biological invasions. Further consideration of these issues may guide the development of strategic responses to D. citri's ongoing invasion.

Highlights

  • Urban ecosystems provide a suite of services for human health and well-being, including food production from urban gardens and commercial agriculture [1,2,3]

  • We obtained a georeferenced database of 78,000 D. citri panel trap collection sites in Southern California from the California Department of Food and Agriculture (CDFA) and the Citrus Pest and Disease Prevention Program (CPDPP) via the Citrus Research Board (CRB) from 2008 through 2014

  • The earliest commercial citrus detection occurred in April 2011, with six additional groves having detections in that year, an additional 208 groves in 2012, and the remainder in 2013 and 2014

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Summary

Introduction

Urban ecosystems provide a suite of services for human health and well-being, including food production from urban gardens and commercial agriculture [1,2,3]. Such benefits should be weighed against potential disservices created as a result of these human-altered landscapes [4, 5]. Most studies have focused on asymmetric movement of insects between agricultural areas and surrounding natural habitats [13, 15, 17] Landscape features, such as the extent and characteristics of habitat edges and the relative proximity to source habitats, have been shown to affect spillover across habitats [13]. Such spillover events can further influence community dynamics of the recipient habitat through processes such as parasitism, predation, and disease transmission [13, 14, 18, 19]

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