Search bioRxiv⌕ Search

bioRxiv · 10.1101/2024.04.24.590937

Bee pasture as a buffer against flower-mediated disease transmission

Abstract

Bees play a crucial role as pollinators in ecosystems, yet they face the risk of flower-mediated diseases that can spread among their communities. Infected bees can inadvertently transmit infective agents, such as microbial spores, to other bee colonies through shared floral resources during foraging. To address this challenge, we propose a solution involving the strategic planting of bee pasture as buffer zones around foraging areas, coupled with the careful placement of beehives to segregate bee colonies. However, this strategy presents dual potential outcomes: the buffer zone could act as a protective barrier, reducing disease transmission; or attract more bees from other colonies, thereby increasing infection risk. Employing mathematical modeling, we explore the intricate dynamics of this strategy to minimize negative outcomes, considering factors such as colony strength, optimal foraging behavior, and foraging area locations. Our results recommend implementing the following measures to safeguard the target bee colony against disease: (i) ensuring ample food sources are available in the vicinity of the target bee colony, and (ii) establishing bee pasture in a distinct, outlying area to serve as a buffer zone. While the bee pasture buffer zone cannot guarantee complete immunity from infection, it can effectively delay the spread of inter-colony diseases. This proposed strategy should be combined with other sound beekeeping practices for comprehensive disease management. Our analysis aims to provide insights into optimizing practices to protect the health of both managed and wild bee populations, and bolster ecological resilience. Significance StatementBees, vital pollinators in ecosystems, face the risk of flower-mediated diseases transmitted between colonies. Flower-mediated disease transmission occurs when bees spread pathogens to each other through sharing of flowers during foraging. To mitigate this, we propose planting bee pasture buffer zones around foraging areas. Using mathematical modeling, we recommend ensuring nearby food sources for the target bee colony and establishing bee pasture buffers. While not guaranteeing immunity, this strategy can delay disease spread. Combining this with other beekeeping practices can comprehensively manage diseases. This research underscores the importance of bee pasture areas for protecting both managed and wild bee populations and strengthening ecosystem resilience. MSC Classification92-10, 92D40, 92D30

Explore related subjects

Keep this discovery

Explore connections, maps & timelines

BibTeXRIS

Rabajante, J. F.. 2024-04-28. Bee pasture as a buffer against flower-mediated disease transmission. https://doi.org/10.1101/2024.04.24.590937

Cite the original work for its findings. Save a collection to share your selection of sources.

KEEP EXPLORING

Related preprints

Wildfires drive trade-offs in ammonia-oxidizing groups and promote denitrification to increase soil emissions of nitric oxide (NO) and nitrous oxide (N2O) in California chaparral

Wildfires can promote trade-offs in soil nitrifier and denitrifier communities that affect post-fire nitrogen (N) cycling and emissions of nitric oxide (NO), nitrous oxide (N2O), and dinitrogen (N2). For example, by increasing soil pH and ammonium (NH4+), wildfires could increase the abundance of ammonia-oxidizing bacteria (AOB) over archaea (AOA). Because AOB and AOA process N differently, nitrifier trade-offs may affect N emissions and nitrate (NO3-) supply with downstream effects on denitrifier activity, leading us to ask: Do trade-offs between AOA and AOB abundance and shifts in denitrifying processes influence N emissions over time after wildfire? We selectively inhibited AOA and AOB communities from soil collected over four seasonal time points one year before and after a chaparral wildfire and used stable isotopes to parse denitrifier contributions to N2O emissions. Over one year after the wildfire, soil pH increased from 6.1 to 7.0, soil extractable NH4+ increased 30-fold, NO3- increased 5-fold, and NO2- increased 9-fold. AOB amoA gene copy numbers increased 20-fold one year after fire, while AOA abundance remained unchanged. Post-fire soil NO emissions increased 63-fold over one year, with varied contributions from all nitrifier groups. Soil N2O emissions peaked eight months after fire (2271 {+/-} 634 ng N2O-N g-1 soil), with increased contributions from AOA. Wildfire increased {delta}15NSPN2O and {delta}15NbulkN2O values, suggesting increased N2O reduction to N2. Overall, wildfire increased AOB abundance relative to AOA, promoting nitrification activity and providing intermediates to denitrifiers to increase emissions of NO and N2O for up to one year after fire.

ecology↗

Global urban forest cover and nature access is insufficient for human wellbeing and worsening

Target 12 of the Global Biodiversity Framework urges governments to enhance human access to nature to improve human wellbeing. Here, we study nature access using several metrics for a globally representative sample of 140 large Functional Urban Areas, examining variation among regions and over time. We find most urbanites globally do not reach common benchmarks for urban forest cover and nature access. Globally, 3.3 billion people (76% of urbanites) live in urban areas that do not have at least 30% tree canopy cover. Moreover, 1.1 billion people (23% of urbanites) are farther than 1 km from a park as identified in Open Street Map, and 1.5 billion people (36% of all urbanites) are more than 1 km from a green patch as defined by land cover. Over time, urban nature access has declined. Between 1992 and 2020, most urban residents had an increase in the distance to green patches (63% of urbanites increased, average increase 680 m). Similarly, between 1992 and 2020, 31% of urbanites had a decrease in percent natural cover, while only 1.3% had an increase. We show that the variation among cities or regions in the amount of nature access depends on the metric used and the context. On average, mesic climates have more tree cover than do arid climates, and cities with lower GDP or higher population density tend to have lower natural share than other cities. Our results suggest that global urban nature access is insufficient for supporting human health and worsening over time.

ecology↗

Exploring soil microbes' potential to assess Atlantic Forest restoration trajectories

Soil microbe communities are key indicators of ecosystem recovery, yet their integration into operational restoration monitoring remains limited. We evaluated the potential for benchmarking early Atlantic Forest restoration with reference site-based comparisons using bacteria and fungi. Samples were collected from three geographic clusters and spanned a pasture-restoration-forest land-use gradient. Using metabarcoding, we assessed whether soil microbe community diversity, structure, and functional profiles respond to restoration progress considering influences from spatial arrangement and/or successional stage (determined using NDVI). We found that OTU alpha diversity was not explained by either predictor, whereas the Shannon diversity of bacterial functions declined significantly with increasing NDVI. Bacterial and fungal OTU composition (Bray-Curtis) responded significantly to both NDVI and geographic cluster, as did microbe functional profiles, although only NDVI proved both marginally and conditionally significant. We also found that soil chemical parameters were primarily structured by geographic cluster but not by NDVI, suggesting that many abiotic edaphic conditions reflect soil history rather than current vegetation status. These findings suggest that both microbe taxonomic and functional metrics track revegetation progress and validate eDNA as a scalable, sensitive restoration monitoring framework. Importantly, our results also support the use of reference site-based monitoring for Atlantic Forest restoration.

ecology↗