Last summer, we started a project comparing the visitation
rates of honeybees and other, mostly solitary pollinators to flower patches of
different sizes. We simultaneously collected data about the potential rewards
of those patches from their peak flowering season well into floral senescence. We got some
interesting
results: first, we found that honeybees visited the larger patches per flower
more frequently than the smaller patches, while other pollinators visited each
at an equal rate. This was consistent with research
suggesting that honeybees can converge on the best resources via
information-sharing within the colony. But do honeybees respond to long-term
seasonal declines across an entire habitat? We found that while solitary
pollinators ceased visiting all resources as blooms senesced – perhaps as a
result of synchronized foraging seasons – honeybees persisted in foraging. Though
they responded to declining value relative to each patch, they did not respond
to the seasonal decline in the larger habitat. This raised some interesting
questions for us: Are honeybee colonies, as information-sharing systems, able
to respond to long-term changes, and how? How are honeybees competing with
other pollinators? How do honeybees, bumblebees and solitary pollinators track
long-term changes in the floral community?
One exciting aspect of springtime field ecology here is the
abundance and diversity of flowering plants – so we can consider these
questions in the context of a complex habitat composed of resources with highly
variable and changing rewards. We planned a project that broadly takes stock of
the reward values of abundant floral resources in a ~50m2 region,
and the visitation rates of various pollinators.
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| [1] Penstemon spectabilis in full bloom |
Every week, we assess the region for abundant and blooming
plants, and select 4-6 species for surveying. We want to track each species
from its earliest flowering date past when it’s no longer a potentially
valuable resource, so we rotate a species off of the list when it ceases
flowering altogether. For each species, we mark four individual patches to
survey that week. We’re using distinctive markers that can be seen aerially by Cassie’s
drone so that we can use our ground data as a training set for detailed
flower maps. Such ground data includes manual flower counts, estimates of
senescence, and nectar samples and sugar content analysis.
As far as pollinator visitation goes, our protocol is the
same as it was last summer: we record visitation for ten minutes at a selected
ten inflorescences at a given patch (inflorescences loosely defined not in
botanical terms, but in terms of how a pollinator would approach the patch, as
this varies quite a bit among plant species). Since our broader research
questions revolve around the differences between solitary and social,
information-sharing pollinators, we sort the pollinators we see into three
categories: honeybees, bumblebees, and others. Honeybees live in large
colonies of 10,000+ individuals, while bumblebees live in small
groups (50-400 individuals in a nest, depending on the species) and other
pollinators are mostly solitary.
We’re coupling the pollinator observations with honeybee
collection – something that we didn’t get the chance to do last summer. The
honeybee collection essentially entails running around with a net and trying
not to get stung when transferring the agitated bee into a vial. By identifying the pollen (using a microscope) carried by honeybees that we collect in the
field, we can get a sense of whether individual foragers are visiting multiple
species of flowers, or just one – and we can relate this to the flowering data
as another way of seeing how honeybees track changes in the composition of
resources.
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[3] a honeybee with pollen baskets
|
It might be interesting to collect pollen from bumblebees
and solitary bees as well, but unfortunately there are far fewer of these than
honeybees, and the destructive sampling isn’t worth it. While there’s been
plenty of hype in the past decade about Colony
Collapse Disorder, less attention has been paid to wide declines in bumblebee and
solitary bee populations. Interest in these declines is growing, but
there’s still a lot that we don’t know. Many
studies find that honeybees, great generalists, are outcompeting and
displacing highly specialized native bees
in their rapidly shrinking habitats. Check back soon to see what we learn about the nature of
competition at variable resources throughout high flowering season at the Bernard Field Station!
Further reading
Kerstin Walther-Hellwig, Gerriet Fokul. “Increased Density
of Honeybee Colonies Affects Foraging Bumblebees. Apidologie 37, 517-532.” Apidologie
37 (2006): 517–32. doi:10.1051/apido:2006035.
Media credits
[1] photo by Matina Donaldson-Matasci
[2] photo by Matina Donaldson-Matasci
[3] public domain image
[2] photo by Matina Donaldson-Matasci
[3] public domain image



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