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Spring 2012
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Date: |
Day: |
Meeting place: |
Time: |
March 24 |
Saturday |
Picnic Point/Lot 129 |
9am-noon |
March 26 |
Monday |
Picnic Point/Lot 129 |
9am-noon |
April 4 |
Wednesday |
Frautschi Point lot |
1:30-3:30pm |
April 12 |
Thursday |
Frautschi Point lot |
1:30-3:30pm |
April 14 |
Saturday |
Frautschi Point lot |
1:30-3:30pm |
April 15 |
Sunday |
Picnic Point/Lot 129 |
9am-noon |
April 17 |
Tuesday |
Frautschi Point lot |
1:30-3:30pm |
April 21 |
Saturday |
Picnic Point/Lot 129 |
9am-noon |
April 22 |
Sunday |
Picnic Point/Lot 129 |
9am-noon |
April 23 |
Monday |
Frautschi Point lot |
1:30-3:30pm |
May 2 |
Wednesday |
Frautschi Point lot |
1:30-3:30pm |
May 4 |
Friday |
Picnic Point/Lot 129 |
9am-noon |
May 5 |
Saturday |
Picnic Point/Lot 129 |
9am-noon |
--celebration |
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Noon-1pm |
May 19—planting |
Saturday |
Picnic Point/Lot 129 |
9am-noon |
May 20—planting |
Saturday |
Picnic Point/Lot 129 |
9am-noon |
For more information on how you can participate in the Challenge please contact:
Bryn Scriver, Preserve Volunteer Coordinator, bscriver@fpm.wisc.edu or 220-5560, or
Roma Lenehan, Friends of the Preserve, rlenehan@charter.net or 238-5406.
On Feb. 22 Preserve staff joined about 40 other conservation professionals and volunteers for a workshop on Wisconsin bumble bees sponsored by the Xerces Society for Invertebrate Conservation and the UW-Madison Arboretum. Jennifer Hopwood of the Xerces Society introduced us to bumble bee ecology, identification and conservation efforts.
The impetus for the workshop came in the fall of 2011, when Arboretum staff documented the presence of Bombus affinus, commonly known as the rusty-patched bumble bee. B. affinus was once common throughout much of the eastern United States and upper Midwest, but its populations have declined dramatically in recent years, and it is now absent from much of its historic range. The same holds true for three other bumble bee species in the U.S. – B. terricola, B. occidentalis,and B. franklini.

Worldwide, pollinators are required for approximately 35% of crop production. Here in Wisconsin, cranberries, apples, green beans, and cucumbers are just some of the crops that require pollination. Wisconsin has 20 species of native bumble bees that are important pollinators for agricultural crops as well as native plant communities. Members of the gentian family are fully reliant on bumble bees to pollinate their flowers, as Bombus species are the only bees strong enough to pry open the tight corolla and wiggle their way down the flower tube.
Bumble bees are active both earlier and later in the day than other pollinators. They accomplish this through muscular thermogenesis – the bumble bee equivalent of jumping jacks – whereby they shiver their flight muscles to create heat. This allows them to be active early in the spring, late in the fall, and on cloudy, damp days, when other pollinators are less likely to be active.
Shivering flight muscles also allow bumble bees to perform buzz pollination (or sonication) of certain flowers, such as cranberries, blueberries, eggplants, tomatoes, and other species in the Solanaceae family. In our prairies and savannas, Midland shooting star (Dodecatheon meadia) also is a benefactor of buzz pollination by bumble bees.
Bumble bees form annual colonies in North America. Queen bees overwinter in the ground, often in insulated locations such as abandoned rodent dens. When the queens emerge in the spring, they begin searching for nest sites. This is the time of year when you’ll often see the plump queens hovering back and forth just above the ground. Once the proper site has been located, the queen begins laying eggs that will form the work force of the colony. Eggs hatch within a couple of days, and the larvae begin to feed on a mixture of pollen and nectar provided by the queen. The larval stage has four instars of development, and the adult bees emerge approximately five weeks later. The first cohort to emerge is comprised entirely of female workers that begin foraging for the colony. Later in the summer, the colony reaches its peak and begins producing males and potential queens, which leave the nest to mate. Mated queens search for sheltered locations and enter diapause to overwinter. The rest of the colony dies as colder temperatures of late fall set in.

Image: http://www.bumblebee.org/
In addition to habitat loss, wild bumble bee populations are increasingly threatened by the spread of disease from commercially produced bees. Changing climate and seasonal phenology may also affect bumble bee survival, as periods of warm weather in early spring may rouse queens from their hibernation before the plants they feed on have emerged.
When managing for bumble bees, one of the most important factors to keep in mind is providing adequate forage throughout each season. Whether it’s in your home garden or a restored prairie, fostering a plant community that provides flowering plants from early spring through late fall will help to ensure that bumble bee colonies are robust during the growing season, and that queens are well fed prior to their winter dormancy. The Lakeshore Nature Preserve with its restored natural areas and extensive organic gardens may be especially attractive for pollinators.
A more thorough review of bumble bee ecology can be found at www.xerces.org/bumblebees
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The Friends of the Lakeshore Nature Preserve July 22 fieldtrip, led by Susan Carpenter, will focus on native pollinators in the Preserve gardens and restored landscapes. For details and a complete list of Friends sponsored field trips go to their website.
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| We want to know which species of bumble bee are buzzing around the Preserve. Please contact Bryn Scriver, bscriver@fpm.wisc.edu to learn techniques for “collecting” bumble bees with your camera. |
The spring of 2011 brought beautiful weather, but winds that prevented prescribed burns from being conducted in the Preserve. Given the Preserve’s location in an urban matrix, the appropriate winds ensure that smoke is dispersed away from University Hospital, Eagle Heights Apartments, and other areas of concern. The lack of burns last spring turned out to be only a minor setback, as it paved the way for the first fall burns conducted in the Preserve’s history.
This spring, Preserve staff plan to build on that success by continuing to expand the use of fire as a management tool in other areas of the Preserve. Several small restoration areas have been planted with fire-adapted prairie plants. Such species thrive under a regular burn regime. Fire serves multiple purposes, including removing leaf litter and thatch, controlling cool-season weeds and tree seedlings, improving germination of native seed, and stimulating growth of fire-dependent plant species – the blackened soil warms faster than unburned areas, accelerating growth of warm-season plants.
Until recently, prescribed burns focused on Biocore Prairie in the heart of the Preserve. Last fall, burn units expanded outside of the prairie to other areas in the western portion of the Preserve. This spring, a number of small burn units are planned in the eastern end of the Preserve. Though these locations pose logistical challenges given the close proximity to buildings, roads, and pedestrian paths, it also provides opportunities for educating the campus community about the importance of fire in land management. Prescribed burns are carried out by trained personnel, and are conducted under conditions that meet the prescriptions laid out in the prescribed burn plan.
To any regular walker, jogger, or passerby of the Lakeshore Nature Preserve, it is a common sight: the pulling, plucking, cutting, yanking, and piling of unwanted vegetation. Whether it is in the form of interns wielding handsaws and clippers poking through the brush, volunteers stuffing black garbage bags full of leafy undesirables, or staff toting plastic “backpacks” of electric blue herbicide, invasive species management is always visible at the Lakeshore Nature Preserve. But what qualifies a plant as “invasive?” Why is so much effort directed at controlling these species, and most importantly, why should users of and visitors to the Lakeshore Nature Preserve be concerned about this issue?
What is an Invasive Species? Plant life in the Preserve can be divided up into three categories: that which is “native,” that which is “non-native,” and that which is “invasive.” Native plants are defined as plants that had already established themselves in North America prior to European settlement or have since arrived by natural means of dispersal. Non-native plant species, on the other hand, are plants that have been introduced by humans, either intentionally or accidentally. While many non-natives don’t pose serious threats to the quality of a native plant community and can even be helpful (take the potato and other food crops, for instance), some can be highly aggressive and harmful; these are known as “invasive” species.
Invasive species aren’t merely nuisances like the occasional weed or dandelion; they are much more disruptive and can negatively impact not only the environment, but also the economy and human health. They tend to have high reproductive rates, produce many seeds, and can cover large areas and persist in them for many years. As a result, they displace native plants through competition for nutrients, sunlight, and pollinators, and decrease biodiversity. Invasive species have no natural controls to keep them in check and therefore tend to decimate and dominate native plant communities; this is why oceans of garlic mustard can often be seen in what was once a diverse woodland plant community. Volunteers and Preserve staff diligently pull, pluck, and cut in an attempt to artificially become those lost biotic controls.
Why Should We Care? Invasive species negatively impact the beauty, health, and functionality of the Lakeshore Nature Preserve. Single species stands of dame’s rocket displace native phlox, and porcelainberry vine engulfs and smothers what could have been viable, native walnut trees. Vibrant natives are replaced by monocultures of tangled and bulky invasives, displacing with them the pollinators, birds, and animals dependent on these plants. Invasive control is so vital to the Preserve because without it, walking, bird watching, enjoying the beauty of natural wildflowers, and hiking would be difficult or impossible. Constant vigilance, and the constant dedication of volunteers of staff, is needed to manage and eliminate these harmful invaders.

University Communications released a story on the improvements to Picnic Point on March 14, 2012. You can read it here http://www.news.wisc.edu/20441.
In addition to the changes made possible by the Ebling Picnic Point fund, volunteers and Preserve staff began removing buckthorn in November 2011, moving west from the project site which at the time was marked by an abrupt dense edge of buckthorn. The initial clearing sought to create a gradual transition between the project site and the surrounding woodland. Through the winter, we have continued removing buckthorn west toward the narrows. The removal efforts will slightly increase views to the lake, decrease competition with native vegetation, and ease access to the area for managing other undesirable species, namely garlic mustard.
In recent years the woodland floor has been mostly devoid of vegetation (lots of bare soil) except for some large patches of trout lily which has persisted in the understory because it’s a spring ephemeral which completes its growing cycle before the leaves open on trees and shrubs. This spring we will plant some shrubs and small trees to replace some of the buckthorn that was removed to maintain cover and food sources for wildlife.
Volunteer groups involved in the clearing since Nov. 2011:
THANK YOU!

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| 03/21/2012 |