Abstract

Abstract Pollinators experience large spatiotemporal fluctuations in resource availability when mass‐flowering crops are rotated with resource‐poor cereal crops. Yet, few studies have considered the effect this has on pollinator population stability, nor how this might be mitigated to maintain consistent crop pollination services. We assess the potential of boundary features (standard narrow 1 m grassy margins, hedgerows and wide 4 m agri‐environment margins) to support and stabilise pollinator populations and pollination service in agricultural landscapes under crop rotation. Assuming a 6‐year rotation, we use a process‐based pollinator model to predict yearly pollinator population size and in‐crop visitation rates to oilseed rape and field bean across 117 study landscapes in England with varying amounts of boundary features. We model both ground‐nesting bumblebees and solitary bees and compare the predictions including and excluding boundary features from the landscapes. Ground‐nesting bumblebee populations, whose longer‐lifetime colonies benefit from continuity of resources, were larger and more stable (relative to the no‐features scenario) in landscapes with more boundary features. Ground‐nesting solitary bee populations were also larger but not significantly more stable, except with the introduction of wide permanent agri‐environment margins, due to their shorter lifetimes and shorter foraging/dispersal ranges. Crop visitation by ground‐nesting bumblebees was greater and more stable in landscapes with more boundary features, partly due to increased colony growth prior to crop flowering. Time averaged crop visitation by ground‐nesting solitary bees was slightly lower, due to females dividing their foraging time between boundary features and the crop. However, despite this, the minimum pollination service delivered was higher, due to the more stable delivery. Synthesis and applications. Field boundary features have an important role in stabilising pollinator populations and pollination service in rotational systems, although maintenance of larger semi‐natural habitat patches may be more effective for stabilising less mobile solitary bee populations. We recommend using combinations of boundary features, accounting for pollinator range when spacing features/rotating crops, and synchronising boundary feature management with crop rotation to maximise their stabilising benefits.

Highlights

  • Pollination is a key ecosystem service to global agriculture, enhancing production in ~75% of global crop species (Klein et al, 2007; IPBES et al, 2016)

  • This study used a validated process-­based model and 117 study landscapes in England to explore the impacts of boundary features on the stability of ground-­nesting bee populations and their associated pollination service under common UK crop rotations

  • Synchronising boundary feature management with crop rotation could extend their stabilising benefits for pollinator populations and pollination service beyond those captured by our simulations, through (a) timing feature management to ensure sufficient floral resources remain when mass-­flowering crops are absent from a field, and (b) scheduling the peak habitat quality of features to encourage the more mobile bumblebee populations to follow rotated mass-­ flowering crops around the farmscape

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Summary

| INTRODUCTION

Pollination is a key ecosystem service to global agriculture, enhancing production in ~75% of global crop species (Klein et al, 2007; IPBES et al, 2016). The growth of mass-­flowering crops, such as field beans Vicia faba and oilseed rape Brassica napus (hereafter OSR) can benefit pollinators, by providing highly abundant resources for those physically able to access them (Holzschuh et al, 2013; Westphal et al, 2003) Their short flowering season rarely covers the entire active period of local pollinators, so life history (whether long-­ lived and colony building, or solitary and short-­lived) affects whether or not corresponding reproductive gains are realised (Riedinger et al, 2015; Westphal et al, 2009). Boundary features could stabilise pollinator populations when resources vary temporally across multiple time-­scales This includes resource time-­scales shorter than the lifetime of individual pollinators (e.g. weekly, where mass-­flowering occurs briefly each year in the same location) and multi-­year time-­scales longer than the lifetime of individual pollinators (e.g. where resource-­rich mass-­ flowering crops only occur in a given field once in a set number of years). We examine how this impacts the level and reliability of crop pollination service, and suggest management approaches for maximising the stabilising effect of field boundary features

| MATERIALS AND METHODS
Findings
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| DISCUSSION
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