Pollination Biology and Insect Visitation of Pasqueflower (Ranunculaceae: Pulsatilla patens ssp. multifida) in the Little Missouri National Grasslands of North Dakota
Joshua W. Campbell1* and Alex R. Morphew1
1US Department of Agriculture, Agricultural Research Service, Northern Plains Agricultural Research Laboratory, 1500 N. Central Ave., Sidney, MT 59270 USA. *Corresponding Author.
Praire Naturalist, Special Issue 1 (2022):1–10
Abstract
The Little Missouri National Grassland, located in western North Dakota, is the largest national grassland in the United States. Little is known about pollinator communities within this region of the northern Great Plains. Pulsatilla patens ssp. multifida (Pasqueflower) is one of the first plants to flower in the early spring. We investigated the pollination biology of the P. patens ssp. multifida through an insect exclusion study and observational surveys to determine if the species is dependent on insects for setting seed and to document the common insect visitors to open flowers. We found that flowers in which insects were excluded from visiting had a lower chance of producing seed heads and developing mature seeds compared with control flowers. However, flowers that did produce mature seeds from both the control and treatment groups produced similar numbers of seeds per flower. The most common likely pollinators were andrenid and halictid bees, specifically genera Andrena and Lasioglossum. Thus, the early spring bee community may be dependent on P. patens ssp. multifida for pollen and nectar due to the lack of other flowering plants duri ng this time period.
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Pollinators of the Great Plains: Ecology, Distribution, and Conservation
2022 PRAIRIE NATURALIST Special Issue 1:N1–o1. 01
Pollination Biology and Insect Visitation of Pasqueflower
(Ranunculaceae: Pulsatilla patens ssp. multifida) in the
Little Missouri National Grasslands of North Dakota
Joshua W. Campbell1* and Alex R. Morphew1
Abstract - The Little Missouri National Grassland, located in western North Dakota, is the largest national
grassland in the United States. Little is known about pollinator communities within this region
of the northern Great Plains. Pulsatilla patens ssp. multifida (Pasqueflower) is one of the first plants
to flower in the early spring. We investigated the pollination biology of the P. patens ssp. multifida
through an insect exclusion study and observational surveys to determine if the species is dependent
on insects for setting seed and to document the common insect visitors to open flowers. We found that
flowers in which insects were excluded from visiting had a lower chance of producing seed heads and
developing mature seeds compared with control flowers. However, flowers that did produce mature
seeds from both the control and treatment groups produced similar numbers of seeds per flower. The
most common likely pollinators were andrenid and halictid bees, specifically genera Andrena and
Lasioglossum. Thus, the early spring bee community may be dependent on P. patens ssp. multifida for
pollen and nectar due to the lack of other flowering plants duri ng this time period.
Introduction
Pulsatilla patens (L.) Mill ssp. multifida (Pritz) Zamels (Pasqueflower or Prairie Crocus),
also known as Anemone patens (L.) ssp. multifida (Pritz) Hulten, is a member of the family
Ranunculaceae and is native to mixed and short-grass prairies, sub-alpine meadows, and dry
rocky areas in North America. This is one of the first spring flowers to bloom in the northern
Great Plains and tundra areas and its range extends broadly from Wisconsin to Alaska and
south as far as Texas. A perennial, P. patens ssp., multifida (hereafter P. patens) produces
showy, bell-shaped flowers consisting of 5–7 light-blue to purple sepals (Van Bruggen 1983).
The center of the flower consists of 150 to 200 yellow stamens and several pistils situated in
the middle of the stamens (Dutton et al. 1997). The outer stamens are modified nectaries (Bock
and Peterson 1975). Flowers open during the day and close at night and during cold days
(Ordway 1986). In general, P. patens is shade-intolerant and relies primarily on early-season
flowering periods and regular disturbances, such as fire and mild grazing to limit competition
for sunlight and nutrients from nearby plant species (Kricsfalusy 2016).
In some portions of the northern Great Plains, P. patens is quite common. However, declines
at the edges of its range have led to elevated conservation status of P. patens in some
states, including Washington and Wisconsin, where it is currently classified as threatened
and endangered, respectively (Fertig 2021, Wisconsin Department of Natural Resources
Bureau of Natural Heritage Conservation 2021). These declines are likely linked to native
prairie habitat loss due to agriculture and shifts in disturbance regimes, such as under- or
over-grazing and fire suppression (Kricsfalusy 2016, Kricsfalusy and Ponomarenko 2013).
Although P. patens can be found in grassland habitats across multiple states/provinces, and
despite growing concern for conservation of the species, very little is known about P. patens
pollination. The few studies documenting insect associates were accomplished in Colorado,
1US Department of Agriculture, Agricultural Research Service, Northern Plains Agricultural Research Laboratory,
1500 N. Central Ave., Sidney, MT 59270 USA. *Corresponding Author: joshua.campbell@usda.gov.
Associate Editor: Clint Otto, US Geological Survey, Northern Prairie Wildlife Research Center.
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Minnesota, North Dakota, and Canada (Ascher and Pickering 2021, Bock and Peterson 1975,
Gibbs 2010, Ordway 1986). P. patens insect visitors can be readily found during early spring
throughout the northern Great Plains. Thus, this plant is important for provisioning pollen and
nectar for early season bees and other pollinators. Within this region is the Little Missouri
National Grassland (LMNG), which is the largest national grassland in the United States.
Administered by the United States Department of Agriculture Forest Service, the LMNG is
located in western North Dakota and comprises over 400,000 ha. Primary studies conducted
in LMNG have thus far focused largely on grasshoppers, birds, and plants (e.g., Branson 2011,
Fontaine et al. 2004). To our knowledge, only one pollinator study has been conducted within
the LMNG, which explored pollinators of Echinacea angustifolia DC (purple coneflower)
(Leuszler et al. 1996). However, one pollinator study was conducted in Theodore Roosevelt
National Park, which is surrounded by the LMNG (Larson et al. 2006). In addition to little
research on pollinators conducted within the LMNG, extensive knowledge gaps exist regarding
pollinators of the northern Great Plains in general (Hanberry et al. 2020).
We investigated P. patens pollination in the LMNG where we conducted surveys of
flower-visiting insects and an insect exclusion experiment. Our objectives were to (1)
document flower-visiting insects and their foraging behavior on P. patens blooms and (2)
determine if P. patens in the LMNG require insect visitation to set seed. Based on prior
research, we anticipated that bees in the family Andrenidae, specifically those in the
genus Andrena Fabricius, would be the most common insect visitors. We hypothesized
that insect excluded flowers would produce fewer seeds compared to flowers that were
allowed insect visitation.
Methods
Site Description and Insect Exclusion Experiment
We located 4 sites within the LMNG that contained numerous P. patens and were
separated by at least 2 km to ensure independent populations (Supplemental Table 1, available
online at https://eaglehill.us/prna-010h-campbell-s1.pdf). All sites were considered
shortgrass prairie, with plant communities composed primarily of Bouteloua gracilis
(Kunth) Lag. ex Griffiths (blue grama), Juniperus horizontalis Moench (creeping juniper),
Schizachyrium scoparium (Michx.) Nash (little bluestem), and Bouteloua dachtyloides
(Nutt.) Columbus (buffalo grass). Prior to bloom (6–9 April 2021), we placed 10
mesh cages over P. patens plants at each site, and these acted as our insect exclusion
treatment. Plants chosen for the caged treatment had a) at least 1 clearly formed flower
bud, with no visible anthers or petals (i.e., insect pollination not possible), and b) were
within 10 meters of another P. patens plant with a clearly-forming flower. Control or
open-treatment flowers were thus located within 10 meters of a paired, caged plant and
had either a) closed flowers or b) newly-opened flowers. Cages were approximately 30
cm (width) x 30 cm (height), cylindrical, and consisted of aluminum screening with 0.5
mm2 size mesh. Additionally, at each site, we tagged 10 additional P. patens plants to act
as our control treatment (insects could freely visit flowers). In total, 81 stems with clearly
forming flower buds were caged for the insect exclusion treatment, and 107 stems with
either developing or open flowers were tagged for the control treatment.
After flowers senesced, we visited each study plant once every 3 days to assess seed
development. We collected developed seed heads when a majority of the seeds were visually
determined to be near maturation but not yet liberated from the seed head. For each
seed head collected, we counted the number of mature seeds. We considered a seed mature
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2022 Special Issue 1
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if an achene was at least 2 mm long, 1.5–2 mm wide, and attached to an awn (Fig. 1). At
3 of the 4 sites, extensive herbivory of flowers occurred and we established new control
treatments to maintain our 10 replicates per site.
Insect Surveys
We conducted visual insect surveys walking slowly throughout the extent of our focal
P. patens populations. When possible, 2 people conducted surveys at the same time and
location to minimize observer bias. The first surveys began when approximately 10% of
the P. patens within the site were open and the last surveys were made when approximately
90% of flowers had already senesced. When open P. patens were encountered,
we collected representative insects that were actively visiting reproductive parts of the
flower (anthers/pistils). Insects that could not be collected were recorded. All collected
and recorded insects were identified to the lowest taxonomic level possible. All visual
surveys were conducted between the hours of 10:30 and 18:30 on 9 days from April 8
to 13 May 2021. Given that sustained wind speeds averaged 10.2 and 11.2 m/s (23 and
25 mph) in April and May (NCEI 2021), respectively, we were logistically unable to
limit surveys to periods of minimal wind speeds. Thus, surveys took place when weather
conditions were a minimum of 10°C and winds were less than 9 m/s (20 mph). Lengths
of individual surveys ranged from 10 to 70 minutes and were largely driven by weather
conditions and flower abundance.
In addition to visual insect surveys, on 4 separate days (21, 22, 30 April; 14 May),
digital video cameras (Sony HD Handy Cams) attached to tripods recorded blooming P.
Figure 1. A) Andrena sp. visiting the of an early spring P. patens. B) P. patens achene and plumose
awn.
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patens. Cameras were placed approximately 30 cm from flowers. We later watched each
video and recorded flower visitors and length of time they remained on the flower. Only
insects that touched anthers or pistils were counted.
We also conducted a literature search to document all flower-visiting insects
previously observed on or collected from P. patens. In addition to reviewing primary
literature, we searched the Discover Life database (Ascher and Pickering 2021) for
digital records of insects collected directly from P. patens, P. patens ssp. multifida, A.
patens, and A. patens ssp. multifida.
Statistical Analysis
A chi-square test was used to determine if the likelihood of producing a seed head
was different between caged and control treatments. Aborted seeds were excluded from
these analyses. Due to the non-normality of the data, a Wilcoxon Rank Sum test was used
to test for differences between the amount of time Lasioglossum Curtis (sweat bees) and
Andrena Fabricius (mining bees) spent on individual flowers based on the video survey
and for the number of mature seeds produced between the caged and control treatments.
Results
Insect Exclusion Experiment
A total of 35 P. patens flowers developed on plants within cages, and 71 flowers developed
on the plants in the control treatment. However, only 62% of flowers under cages produced
seed heads (n = 22) whereas 83.1% of flowers in the control treatment produced seed
heads (n = 59). The Chi-square analysis revealed that control plants that were allowed insect
visitation to flowers were significantly more likely to produce seed heads (χ² = 14.72, df = 1,
P = 0.0001) than caged plants. Additionally, only 27.2% of all plants from the insect exclusion
treatment produced mature seeds, whereas 38.2% of all plants in the control treatment
produced mature seeds (Fig. 2A). An average of 20.1 (SE ±3.5) mature seeds developed
from flowers within the insect exclusion treatment and an average of 17.8 (SE ±2.9) mature
seeds in the flowers from the control treatment, but this difference was not statistically different
(z = 0.78, P = 0.44) (Fig. 2B). Over the course of the study, we observed widespread
herbivory of mature flowers at 3 of the 4 sites. At the fourth site, however, we found no
evidence of herbivory. A total of 36.4% of the original open treatment flowers were grazed
for the other 3 sites.
Figure 2. Proportion of mature seeds produced from flowers between the caged and control treatments (A)
and the mean number of mature seeds (± SE) produced from insect excluded plants (caged) and plants allowed
insect visitation (control) (B).
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Insect Surveys
A total of 526 minutes and 117 flower-visiting insects were recorded on video. Bees
(Apoidea) were the most common insects recorded (n = 56) followed by ants (Formicidae)
(n = 39). Of bees, the genus Andrena was most common (N=39) followed by the genus
Lasioglossum (n = 18). On average, Lasioglossum spent more time on individual flowers
(92.9 seconds) compared to Andrena (46.9 seconds; Z = 3.02, P = 0.0025, Figure 3).
We conducted a total of 640 minutes of visual surveys and collected/observed 81
insects. Again, bees were among the most common flower visitors (n = 43), followed by
flies (n = 17), and ants (n = 11). Of the bees, Andrena (n = 32) and Lasioglossum (n = 10)
were the most frequently observed genera, and 15 of the 17 observed flies were tachinids
in the genus Winthemia Robineau-Desvoidy (Tachinid fly) (N = 15). See Table 1 for a list
of all insects documented on video and observational surveys. Diptera and Formicidae individuals
were identified by J.W. Campbell (Fisher and Cover 2007, Miranda et al. 2013).
Collected Andrena and Lasioglossum bees were identified to species by A.R. Morphew
and M. Arduser (Bouseman and LaBerge 1979; Gibbs 2010, 2011; LaBerge 1985, 1986;
LaBerge and Ribble 1975).
P. patens-associated insect records documented in the literature spanned 5 insect orders
and included 6 families of Hymenoptera (Table 2). Bees were by far the most common
visitors observed in this study and 8 bee genera overall have been reported visiting
P. patens flowers. Discover Life database records for P. patens insect visitors contributed
an additional 10 bee species, all of which were collected from P. patens between the years
1906 and 1915.
Figure 3. Mean duration of flower visit in seconds by Andrena and Lasioglossum, determined using video
footage. Error bars represent the standard error. Photos of Andrena carlini (left) and Lasioglossum (Dialictus)
pruinosum (right) used with permission from and taken by Sam Droege/www.discoverlife.com.
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Discussion
P. patens is one of few species that can be found flowering during early spring in the
northern Great Plains, making it an important resource for flower-visiting insects. Despite
this, very few studies have assessed the flower-visiting insects and pollination of P. patens. In
this study, we documented numerous insect visitors to P. patens flowers. Overall, the number
of developed seeds produced by control (open) P. patens was significantly higher than that
of caged, insect-excluded plants. Thus, our data suggests that P. patens benefit from insect
visitation that is probably promoting cross pollination. In addition to the reproductive benefit
to P. patens, insect visitors are being supplied floral resources that sustain adults and larvae.
Only a few Townsendia Hook (Townsend daisies) plants were observed flowering during the
bloom period for P. patens, exemplifying the importance of P. patens to early-season bees and
other insects dependent on pollen/nectar.
Although bees and other insects undoubtedly contribute to cross pollination, numerous
plants within our insect exclusion cages produced seed heads with mature seeds. Due to potential
harsh weather conditions, P. patens has probably evolved the ability to self-pollinate
when insect activity is low. Additionally, andrenid bees were observed visiting P. patens on
Family/Taxa Genera/Taxa Video
Visual/Collecting
Surveys
Coleoptera Chrysomelidae 4 1
Diptera muscoids 6
Syrphidae Copestylum Mcquart sp. 1
Paragus Latreille sp. 2
Platycheirus Lepeletier and Serville sp. 1
Tachinidae Winthemia spp. 5 15
Hemiptera Miridae Lygus Hahn spp. 1 9
Hymenoptera Andrenidae Andrena spp. 39 16 (not collected)
Andrena (Euandrena) algida Smith ♀, ♂ 8
Andrena (Melandrena) carlini Cockerell ♀, ♂ 6
Andrena (Holandrena) cressonii Robertson ♂ 1
Andrena (Thysandrena) w-scripta Viereck ♀ 1
Halictidae Halictus confusus Smith ♀ 1 1
Lasioglossum (Dialictus) pruinosum Robertson ♀ 4
Lasiolgossum (Dialictus) laevissimum Smith ♀ 1
Lasioglossum(Dialictus) Robertson sp. 1 ♀ 1
Lasioglossum (Hemihalictus.) sp. 1 ♀ 2
Lasioglossum spp. ♀, ♂ 18 2 (not collected)
Formicidae includes Tapinoma sessile Say and Formica L. spp. 39 11
Lepidoptera Papilionidae Papilio polyxenes Fabricius (Black Swallowtail) 1
Total P. patens Visitors 117 81
Table 1. List and numbers of all P. patens visitors observed visiting open flowers from digital video
and visual/collecting surveys. All insects were observed between 8 April – 14 May 2021 in the Little
Missouri National Grassland, North Dakota.
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Order Family Species State Reference or
Collection
Year
collected
Hymenoptera Andrenidae Andrena spp. CO Bock and Peterson 1975 1971-1973
MN Ordway 1986 1984
Andrena (Parandrena)
andrenoides Cresson
Unk. Krombein et al. 1979 Unk.
Andrena (Euandrena) algida CO *AMNH_BEE;
*UCRC_ENT
1913;
1906, 1913
ND *AMNH_BEE;
*CUIC_ENT
1913
Andrena (Melandrena) carlini MN Ordway 1986 1984
Andrena (Holandrena)
cressonii
CO *AMNH_BEE;
*UCRC_ENT
1913; unk.
Andrena (Tylandrena)
erythrogaster Ashmead
MN Ordway 1986 1984
Andrena (Trachandrena
mariae Robertson
MN Ordway 1986 1984
Andrena (Trachandrena)
sigmundi Cockerell
MN Ordway 1986 1984
Andrena (Scrapteropsis)
nigra Provancher
MN Ordway 1986 1984
Andrena (Larandrena)
miserablis Cresson
MN Ordway 1986 1984
Andrena (Scrapteropsis)
imitatrix Cresson
MN Ordway 1986 1984
Andrena (Micandrena)
Ashmead sp.
MN Ordway 1986 1984
Apidae Apis mellifera L. CO Bock and Peterson 1975 1971-1973
MN Ordway 1986 1984
Ceratina neomexicana
Cockerell
CO *AMNH_BEE 1913
Ceratina Latreille sp. MN Ordway 1986 1984
Bombus Latreille spp. CO Bock and Peterson 1975 1971-1973
Epeolus Latreille sp. MN Ordway 1986 1984
Halictidae Halictus Latreille sp. MN Ordway 1986 1984
Halictus (Halictus)
rubicundus Christ
Unk. Moure and Hurd 1987 Unk.
CO *AMNH_BEE
*AMNH_BEE
1906; 1913
ND 1913
Lasioglossum sp. MN Ordway 1986 1984
Lasioglossum Dialictus)
admirandum Sandhouse
ND *AMNH_BEE 1915
Table 2. Known insect visitors of P. patens. Species records associated with entomology collections
were taken from the Discover Life database (Ascher and Pickering 2021) and are indicated with an
asterisk (*). AMNH_BEE: American Museum of Natural History; CUIC_ENT: Cornell University
Insect Collection Database; UCRC_ENT: University of California, Riverside, Entomology,
Entomology Research Museum.
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Lasioglossum Dialictus)
cinctipes Provancher
CO *AMNH_BEE 1913
Lasioglossum Dialictus)
cressonii Robertson Canada Gibbs 2010 Unk.
Lasioglossum Dialictus)
laevissimum Smith
ND *AMNH_BEE 1915
Lasioglossum
Dialictus) pilosum Smith Canada Gibbs 2010 Unk.
Lasioglossum
Dialictus) pruinosum
ND *AMNH_BEE 1915
Lasioglossum Dialictus)
semicaeruleum Cockerell
ND *AMNH_BEE 1913
Lasioglossum s.s.) sisymbrii
Cockerell
CO *AMNH_BEE 1913
Colletidae Colletes Latreille sp. MN Ordway 1986 1984
Formicidae Formica obscuripes Forel MN Ordway 1986 1984
Tenthredinidae MN Ordway 1986 1984
Diptera Syrphidae CO Bock and Peterson 1975 1971-1973
Anthomyiidae MN Ordway 1986 1984
Tachinidae MN Ordway 1986 1984
Hemiptera Miridae MN Ordway 1986 1984
Scutellaridae MN Ordway 1986 1984
Coleoptera MN Ordway 1986 1984
Thysanoptera MN Ordway 1986 1984
Table 2. Continued.
cool, windy days suggesting they too have evolved to forage in sub-optimal weather conditions.
Indeed, Andrenidae have been documented to forage in cooler weather (Herrera 1995)
or weather that is unsuitable for honey bees (Güler and Sorkun 2010).
Published records for P. patens-visiting insects included numerous bee species, flies,
ants, and many other insects (Table 2). Bees were, by far, the most commonly observed
insect-visitors, with Andrena bees comprising a majority of these observations. Andrena are
usually the first bees to emerge from their ground nests in the spring. Due to their larger size
(compared to Lasioglossum) and their shorter visitation time per flower, and thus increased
likelihood of visiting multiple flowers, they are probably the most efficient pollinator of
P. patens. Andrena bees were also the most commonly observed visitors of P. patens from
other observational studies (Table 2; Bock and Peterson 1975, Ordway 1986). Overall, 12
species of Andrena have been documented on P. patens (Tables 1 and 2). Of these, 4 Andrena
species were observed during this study, including Andrena w-scripta, a previously
unknown P. patens association prior to this study.
Lasioglossum and Winthemia were also both observed visiting multiple plants, thus
probably also contributing to cross-pollination. Ants were also a commonly observed insect
visitor to P. patens. Although ant pollination has been documented in a few plants (e.g.,
Abbate and Campbell 2013), ants are generally considered poor pollinators because they
secrete chemical substances that decrease pollen viability (Beattie et al. 1984). It is also
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unlikely that ants carried many pollen grains and visited multiple plants. Other visitors, such
as Chrysomelidae Latreille (leaf beetles) and Miridae Hahn (plant bugs) are herbivores and,
although they could contribute to pollination, they are likely damaging flowers through herbivory.
The extensive herbivory observed in 3 of our sites was not expected. Often, P. patens
can be found on overgrazed pastures because it is not preferred by livestock (Wildeman and
Steeves 1982). In boreal forests where cattle grazing has ceased, P. patens can become rare
due to increased understory vegetation (Kalliovirta et al. 2006). Antilocapra americana
Ord (Pronghorn Antelope) and Odocoileus hemionus Rafinesque (Mule Deer) were the only
large herbivores that were commonly observed near our sites, and we believe they removed
many of the P. patens during the study. Flowers appeared eaten from above, and often, only
the flower stalk was consumed. Our data suggests that P. patens were also an important early
spring food source for large herbivores.
Our 2 observational methods, visual surveys and video recordings, documented the same
common insect genera (e.g., Andrena, Lasioglossum, etc.) visiting P. patens. Our total visual
survey time included 100 more minutes over 5 additional days than the video recordings.
However, the video recordings documented more insect visits and different insect groups
than observational surveys (Table 1). Thus, some insects may have been wary of researcher
activity and, thus, were not observed during the visual surveys. Future studies that want to
quantify general insect visitation to plants may consider relying on digital recordings of
flower visitors. However, visual surveys and insect collection are essential for species-level
determinations, as digital recordings may currently be insufficient for the identification of
smaller pollinators to species.
Acknowledgements
We thank Avery Pearson and Natalie West for assisting with visual surveys for P. patens insects.
We thank the McKenzie Ranger District of the US Department of Agriculture Forest Service for granting
access and permission to conduct this research and collect insects and P. patens. We gratefully
acknowledge Mike Arduser for bee taxonomic assistance.
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