Abstract

No Mow May is a community science initiative popularized in recent years that encourages property owners to limit their lawn mowing practices during the month of May. The goal of No Mow May is to provide early season foraging resources for pollinators that emerge in the spring, especially in urban landscapes when few floral resources are available. We worked with the city council of Appleton, Wisconsin, USA. to allow No Mow May to take place in May 2020. Four hundred and thirty-five property owners registered for No Mow May in Appleton. We measured floral and bee richness and abundance in the yards of a subset of homes (N = 20) located near regularly mowed urban parks (N = 15) at the end of the month. We found that homes that participated in No Mow May had more diverse and abundant flora than regularly mowed green spaces throughout the city. No Mow May homes had three times higher bee richness and five times higher bee abundances than frequently mowed greenspaces. Using generalized linear models, we found that the best predictor of bee richness was the size of the designated unmowed area, and the best predictors of bee abundances were the size of the unmowed area as well as floral richness. While our findings cannot conclusively attribute increases in bee abundances and richness to the No Mow May efforts, our data does show that bee pollinators make use of no mow spaces as key floral resources during early spring in the upper midwestern United States. A post-No Mow May survey revealed that the participants were keen to increase native floral resources in their yards, increase native bee nesting habitat, reduce mowing intensities, and limit herbicide, pesticide, and fertilizer applications to their lawns. The No Mow May initiative educated an engaged community on best practices to improve the conservation of urban pollinators in future years.

Highlights

  • As landscapes become increasingly urbanized, biodiversity is threatened by land use modifications, a changing climate, and poor management practices (Elmqvist, Zipperer & Güneralp, 2016)

  • The most common and abundant floral resources in lawns and greenspaces are reported in Table 1, with Taraxacum officinale, the common dandelion, present in all home lawns and at 73% of urban park lawns, making it the most abundant plant and floral resource in lawns (Table 1)

  • Melissodes bimaculatus, Apis mellifera, and Bombus impatiens which accounted for 65% of all observed individuals

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Summary

Introduction

As landscapes become increasingly urbanized, biodiversity is threatened by land use modifications, a changing climate, and poor management practices (Elmqvist, Zipperer & Güneralp, 2016). In order to protect as much biodiversity as possible, urban landscapes must be a careful balance of natural habitats, managed urban greenspaces (often consisting of large lawn areas), and functional urban spaces (i.e., spaces that can provide recreational services while maintaining healthy ecosystems) that can accommodate many species (Shochat et al, 2010). These urban areas can be essential for protecting the hundreds of native bee species through supplementing foraging resources for both native and non-native species that provide ecosystem services

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