Abstract:Wild bees are important pollinators of wild plants and agricultural crops and they are threatened by several environmental stressors including emerging pathogens. Honey bees have been suggested as a potential source of pathogen spillover. One prevalent pathogen that has recently emerged as a honey bee disease is the microsporidian Nosema ceranae. While the impacts of N. ceranae in honey bees are well documented, virtually nothing is known about its effects in solitary wild bees. The solitary mason bee Osmia bi… Show more
“…The effects of microsporidia infections in honeybees and bumblebees includes wing deformity, reduced foraging efficiency, reduced colony fitness and increased mortality, with N. bombi being found in multiple species of bumblebees and N. ceranae found in bumblebees and honeybees 65 – 71 In addition N. ceranae may be able to infect the mason bee, Osmia bicornis 72 . While this study did not find impacts on survival, a similar study that assessed impacts of N. ceranae on larval O. bicornis did find negative impacts on survival 73 . The trypanosomatids are mostly Crithidia species whose cells are transmitted via the fecal-oral route.…”
Pollinator declines can leave communities less diverse and potentially at increased risk to infectious diseases. Species-rich plant and bee communities have high species turnover, making the study of disease dynamics challenging. To address how temporal dynamics shape parasite prevalence in plant and bee communities, we screened >5,000 bees and flowers through an entire growing season for five common bee microparasites (
Nosema ceranae
,
N. bombi
,
Crithidia bombi
,
C. expoeki
and neogregarines). Over 110 bee species and 89 flower species were screened, revealing 42% of bee species (12.2% individual bees) and 70% of flower species (8.7% individual flowers) had at least one parasite in or on them, respectively. Some common flowers (e.g.,
Lychnis flos-cuculi
) harboured multiple parasite species, whilst others (e.g.,
Lythrum salicaria
) had few. Significant temporal variation of parasite prevalence in bees was linked to bee diversity, bee and flower abundance, and community composition. Specifically, we found that bee communities had the highest prevalence late in the season, when social bees (
Bombus
spp. and
Apis mellifera
) were dominant and bee diversity was lowest. Conversely, prevalence on flowers was lowest late in the season when floral abundance was the highest. Thus, turnover in the bee community impacted community-wide prevalence, and turnover in the plant community impacted when parasite transmission was likely to occur at flowers. These results imply that efforts to improve bee health will benefit from promoting high floral numbers to reduce transmission risk, maintaining bee diversity to dilute parasites, and monitoring the abundance of dominant competent hosts.
“…The effects of microsporidia infections in honeybees and bumblebees includes wing deformity, reduced foraging efficiency, reduced colony fitness and increased mortality, with N. bombi being found in multiple species of bumblebees and N. ceranae found in bumblebees and honeybees 65 – 71 In addition N. ceranae may be able to infect the mason bee, Osmia bicornis 72 . While this study did not find impacts on survival, a similar study that assessed impacts of N. ceranae on larval O. bicornis did find negative impacts on survival 73 . The trypanosomatids are mostly Crithidia species whose cells are transmitted via the fecal-oral route.…”
Pollinator declines can leave communities less diverse and potentially at increased risk to infectious diseases. Species-rich plant and bee communities have high species turnover, making the study of disease dynamics challenging. To address how temporal dynamics shape parasite prevalence in plant and bee communities, we screened >5,000 bees and flowers through an entire growing season for five common bee microparasites (
Nosema ceranae
,
N. bombi
,
Crithidia bombi
,
C. expoeki
and neogregarines). Over 110 bee species and 89 flower species were screened, revealing 42% of bee species (12.2% individual bees) and 70% of flower species (8.7% individual flowers) had at least one parasite in or on them, respectively. Some common flowers (e.g.,
Lychnis flos-cuculi
) harboured multiple parasite species, whilst others (e.g.,
Lythrum salicaria
) had few. Significant temporal variation of parasite prevalence in bees was linked to bee diversity, bee and flower abundance, and community composition. Specifically, we found that bee communities had the highest prevalence late in the season, when social bees (
Bombus
spp. and
Apis mellifera
) were dominant and bee diversity was lowest. Conversely, prevalence on flowers was lowest late in the season when floral abundance was the highest. Thus, turnover in the bee community impacted community-wide prevalence, and turnover in the plant community impacted when parasite transmission was likely to occur at flowers. These results imply that efforts to improve bee health will benefit from promoting high floral numbers to reduce transmission risk, maintaining bee diversity to dilute parasites, and monitoring the abundance of dominant competent hosts.
“…Considering solitary bees, knowledge about their natural and healthy microbiomes advanced in the recent years [ 19 , 20 , 21 , 22 , 23 , 24 ]. Studies investigating potential microbial pathogens, however, focused on infections that are common between honey bees or bumble bees and solitary bees [ 25 , 26 , 27 ]. While studies investigated non-lethal endosymbionts in solitary bees, e.g., Wolbachia [ 28 ], dedicated studies screening for potential bacterial pathogens and other harmful bacteria in solitary bees specifically are currently lacking.…”
Solitary bees are subject to a variety of pressures that cause severe population declines. Currently, habitat loss, temperature shifts, agrochemical exposure, and new parasites are identified as major threats. However, knowledge about detrimental bacteria is scarce, although they may disturb natural microbiomes, disturb nest environments, or harm the larvae directly. To address this gap, we investigated 12 Osmia bicornis nests with deceased larvae and 31 nests with healthy larvae from the same localities in a 16S ribosomal RNA (rRNA) gene metabarcoding study. We sampled larvae, pollen provisions, and nest material and then contrasted bacterial community composition and diversity in healthy and deceased nests. Microbiomes of pollen provisions and larvae showed similarities for healthy larvae, whilst this was not the case for deceased individuals. We identified three bacterial taxa assigned to Paenibacillus sp. (closely related to P. pabuli/amylolyticus/xylanexedens), Sporosarcina sp., and Bacillus sp. as indicative for bacterial communities of deceased larvae, as well as Lactobacillus for corresponding pollen provisions. Furthermore, we performed a provisioning experiment, where we fed larvae with untreated and sterilized pollens, as well as sterilized pollens inoculated with a Bacillus sp. isolate from a deceased larva. Untreated larval microbiomes were consistent with that of the pollen provided. Sterilized pollen alone did not lead to acute mortality, while no microbiome was recoverable from the larvae. In the inoculation treatment, we observed that larval microbiomes were dominated by the seeded bacterium, which resulted in enhanced mortality. These results support that larval microbiomes are strongly determined by the pollen provisions. Further, they underline the need for further investigation of the impact of detrimental bacterial acquired via pollens and potential buffering by a diverse pollen provision microbiome in solitary bees.
“…Most bee species within a community can be exposed to numerous pathogens when foraging at flowers, including C. bombi (Figueroa et al ., 2020; Graystock et al ., 2020). Our results support a growing body of literature indicating the need to assess the host range of bee pathogens, including assessments of replication and impacts on survival (Bramke et al ., 2019; Müller et al ., 2019). The presence of C. bombi in bee feces has been used to identify active infections in bumble bees (Imhoof and Schmid-Hempel, 1999), where it can be detected in as quickly as 5 days post-inoculation (Logan et al ., 2005).…”
Section: Discussionmentioning
confidence: 99%
“…This includes pathogens known to infect honey bees and bumble bees (Apidae), including Apicystis bombi , Ascosphaera spp., C. bombi , C. mellificae , N. ceranae and numerous viruses (Singh et al ., 2010; Evison et al ., 2012; Ravoet et al ., 2014; Schoonvaere et al ., 2018; Figueroa et al ., 2020). However, except for single-stranded RNA viruses which allow for strand-specific PCR assays to detect viral replication, we currently cannot distinguish between transient passage through the bee gut and active infections, nor do we know if there are negative consequences for the host based solely on molecular screenings (Bramke et al ., 2019). Some existing studies that have experimentally evaluated the impacts on solitary bee health have shown increased mortality associated with infections [e.g.…”
Section: Introductionmentioning
confidence: 99%
“…Some existing studies that have experimentally evaluated the impacts on solitary bee health have shown increased mortality associated with infections [e.g. Megachile rotundata larvae infected with the fungus Ascosphera aggregata (James, 2005) and Osmia bicornis infected with the neogregarine A. bombi and the microsporidian N. ceranae (Tian et al ., 2018; Bramke et al ., 2019)], further highlighting the need to address the host range of bee pathogens and negative consequences for these understudied bee species.…”
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