Tom's Blog

Wednesday, October 4, 2017

Bur oak blight at Pleasant Valley Conservancy

This year, apparently for the first time, a small number of our bur oaks have acquired bur oak blight, a relatively new bur oak disease. The disease is shown in the leaves and symptoms first appeared at Pleasant Valley Conservancy in early August. Infected leaves exhibit purple-brown lesions along the veins on the under side of the leaves. These lesions gradually expand and in many cases the leaf turns completely brown. During the summer, black fruiting structures of the causal agent, the fungus Tubakia iowensis, appear and are diagnostic for the disease.

The disease was first discovered in Iowa by Harrington and co-workers in the 1990s, and is now known to be present also in Minnesota, Illinois, and Wisconsin. This is the first year we have noticed it at Pleasant Valley Conservancy.

Apparently the disease occurs only on bur oaks. There are several subspecies of bur oak in the Midwest, and the disease has only been observed on Quercus macrocarpa var. oliviformis, a variety of bur oak that produces smaller acorns. Interestingly, it was because of this connection that we first noticed that some of our bur oaks are the small-acorn variety.

It is not clear whether this new pathogen is a recent arrival to the Midwest, or whether a shift in climate may be responsible. Apparently the symptoms develop more commonly when the humidity is high. Since we had a rainy summer, this may be partly responsible for its presence at Pleasant Valley Conservancy.

To be certain that we did indeed have bur oak blight, we had infected leaves analyzed at the UW-Madison Plant Disease Diagnostic Laboratory. The report was positive for blight but negative for oak wilt, a more common oak disease (but not very common in bur oaks).
Bur oak leaf turning brown



Typical infestation of bur oak blight



Dark spots on the underside veins are typical of bur oak blight


To get an idea of the extent of the problem at Pleasant Valley Conservancy, I had Amanda and Susan do a survey of our bur oaks. It is fairly easy to recognize an infected tree because of the presence of brown leaves. Since each tree in our database is numbered, and we have its GPS coordinates, I was able to create a map showing the distribution of the disease. As the map shows, most of the infected trees were in a single location, at the upper edge of the North Woods (Units 15 and 19B), and nearby in Units 8 and 10.

The blue dots show the distribution of bur oaks at Pleasant Valley Conservancy, and the yellow dots are those that are infected. The red lines show the location of the Service Road.





We will of course be monitoring our bur oaks next year and later. We hope that the disease is not fatal, because one of our patriarch bur oaks at the top edge of the North Woods is heavily infected and is defoliating.

The U.S. Forest Service has a brochure on bur oak blight which is available on line. Also, the scientific paper describing this disease in detail can be downloaded at the following link:



Saturday, September 23, 2017

Black walnut: one of the bad guys in oak savanna restoration



One of the important parts of our savanna restoration work has been the removal of a large number of black walnuts (Juglans nigra). Although black walnut is considered a cash crop in forestry, it is an invasive species as far as we are concerned.

Walnut was absent from the original land surveyor’s records for our area, indicating that it was only a minor component of the original vegetation. Because it is relatively fire sensitive, it would not have been a major component of the savanna. Black walnut is primarily a tree of the mid-continent of the United States and is at the northern edge of its range in southern Wisconsin. Here it is usually found in mixed forests as single isolated specimens, although in some restricted areas it may become dominant or subdominant.

Black walnut toxicity Black walnut produces a toxic substance called juglone (5 hydroxy-1,4-napthoquinone), which occurs in all parts of the black walnut plant. Juglone inhibits the growth of many other plants, a phenomenon called allelopathy. However, tests have shown that many plants are resistant to juglone and are thus able to grow in the presence of black walnuts. Resistant plants include all grasses, and a number of woodland forbs, including jack-in-the-pulpit, bellflower, bellwort, dutchman’s breeches, wild geranium, mayapple, solomon’s seal, bloodroot, and trillium. Also, spiderwort, a common prairie plant, is resistant to juglone. Honeysuckle, an invasive shrub, is also resistant.

Walnut removal at Pleasant Valley We had three areas at Pleasant Valley Conservancy that had large populations of black walnut. The first two were Units 18 and 21, that are on opposite-facing hills that had the same geology. These hills had been in pasture until the mid 1950s, after which they remained as open land. Both hills had some very large bur oaks that had been unaffected by grazing. After grazing ceased, these two hills gradually filled in with woody vegetation, of which black walnut was the most common tree.

The walnuts on Unit 18 were removed in the winter of 2000-2001, leaving behind a handsome stand of mature bur oaks that had survived years of grazing pressure.

The residual selective toxicity of juglone after walnuts are removed may influence the kinds of plants able to become established. It is interesting that in Unit 18, spiderwort, a species known to be tolerant to juglone, developed extensively on the lower slope after the walnuts had been removed, and has remained in large numbers ever since.

Heavy seeding of Unit 18 with native species was done in the fall of 2001, and again in 2003. Also, Unit 18 has been burned annually ever since, and these burns have been very successful burn. Although brambles were a problem, they were dealt with (cut & treat) in 2006 and this hillside has become a fine oak savanna.

Unit 21, on the hill opposite Unit 18, is in the same geological formation and has had the same land-use history. When restoration began in January 2004, the principal trees were black walnut and slippery elm, with a number of small- to medium-sized oaks. The understory was almost pure honeysuckle.

For the Unit 21 work, cold weather and moderate snow cover was favorable for walnut removal, and all of the trees were off the site within a two-week period. Many of the walnut specimens were fairly large, and were good candidates for saw logs (lumber). We took advantage of the solidly frozen ground and had these logs brought down to the town road by a log skidder. Care was taken to avoid disturbance of the soil. There was also a smaller area of large walnut trees in the ravine between Units 12A and 20 and these were cut and skidded over the snow to the road at the same time.

An area of walnuts in Unit 21. There were 25 walnuts here large enough to convert into lumber.


In total, we had 25 logs ranging in length from 9-10 ft and diameter from 14-25 inches. They were taken by a logging truck to a nearby sawmill. (These logs were donated to the Aldo Leopold Foundation, which converted them to lumber for use in their Legacy Center.)


The third walnut area was the marsh that became the Sandhill Crane Wet Prairie. There were over 70 large walnuts in this area, which were cut and donated to a Mount Horeb resident who burned wood as the main source of heat in his home. During a very cold spell in January 2004, this resident used a Bobcat to bring all these logs up to the town road. (This was a barter arrangement: the resident got the logs gratis but did not charge for the extensive work involved.)

Truck load of walnut logs removed from the marsh edge. Over 70 trees were cut at this location.


The Resprout Problem. For most tree species, treatment of the cut stumps with 21% glyphosate prevents resprouting. However, this procedure was not effective for walnuts and extensive resprouting of cut stumps occurred. By the summer of 2002 the walnut stumps on Unit 18 (cut in the winter of 2001) had resprouted extensively. From each stump as many as 20 new shoots had developed, most from the root collar but some from the side of the stump. In January 2003 all of these resprouts were again cut and treated with herbicide. However, many of these stumps resprouted again in the summer of 2003.

It turned out that glyphosate is not too effective with walnut. Switching to triclopyr (Garlon 4; 20% in oil) was the solution. In addition to treating the cut stems, basal bark application was done. Continual monitoring for walnut resprouts has been done, and the problem has been eliminated.





Friday, September 8, 2017

Old-field thistle in an old field

Old-field thistle (Cirsium discolor) is a favorite plant of pollinators and birds. Goldfinches love them, and many wait until the thistle plant is mature (late August or early September) to nest.

At Pleasant Valley Conservancy, old-field thistle has been in our seed mix since restoration work began. However, since this thistle is a biennial, it moves around. Fortunately, seed viability is good, and colonization is generally successful. However, one hardly ever sees first year plants, which generally grow as low-lying rosettes.

The purpose of this post is to show the origin of this thistle's common name.

The east boundary of PVC is adjacent to a neighbor's field that has been used variously to raise cover crops for a near-by organic farming operation. Three years ago, cropping was abandoned, and this field turned almost immediately into an "old field." About three weeks ago, this field was almost a monoculture of Queen Anne's lace. Yesterday when I looked at it, a large number of old-field thistle plants had developed, more thistles than I had ever seen in one place.

This field is within yards of the PVC East Basin, a five acre restored prairie that has scattered old-field thistle plants.Although thistle seeds get around very well, I suspect that most of the "inoculum" for this field came from our East Basin next door.

According to Allen Stokes, who did a detailed study of goldfinch nesting in Lake Wingra marsh in 1944-1946, late-nesting goldfinches work very fast to complete their nest building and raise their young. This makes sense when one considers that in our area the weather could briefly "crash" at any time.

Incidentally, visitors to PVC generally miss completely the East Basin and the adjacent Ridge Prairie, because the main trail leads in the opposite direction. Now would be a good time for a detour in this direction.

The old field full of old-field thistle

Typical old-field thistle plant

Tuesday, September 5, 2017

Labor Day field trip: Now a Pleasant Valley Conservancy tradition

Kathie and I have been leading a Labor Day (1st Monday in September) field trip at Pleasant Valley Conservancy since at least 2002, possibly a year earlier. (I have sign-up lists going back to 2002.) Labor Day seemed to me then, and still does, an ideal time for a trip. Everyone is off work, the prairie grasses are in full bloom, and there are lots of great forbs in bloom.

The attendance that we have been getting seems to agree with me. In 2002 we had 15 attendees, and the number has been increasing ever since. Last year (2016) we had 35 and this year 45, which is the largest we have ever had.

I'm not really bragging about this. It just seems to me that a chance to see a restored oak savanna is something a lot of people are interested in. I'm just happy that Kathie and I are still able to lead this trip. (Although the last few years I have been leading from a Kawasaki Mule.)

Since this has been a wet summer, it is not surprising that the prairie grasses are really lush. The Indian grass and little bluestem on the South Slope were at their peak, and it was a joy to watch them blowing in the wind. Some people don't like a prairie dominated by warm-season grasses. I made the point that in mid-July the South Slope is a forbs-rich prairie, and forbs and prairie grasses get along very well together. See this link for a discussion of this point.

We generally get a few demon botanists on this trip, and this year was no exception. Scott Weber and Muffy Barrett, Chris Noll, and Raymond Roberts were all finding things that Kathie and I did not know we had. The prize this year was northern slender ladies' tresses (Spiranthes lacera), found by Raymond right off the trail. (At PVC last year, a week after Labor Day, Scott had found Spiranthes ovalis, another rarity.) These tiny orchids like disturbed grown, and most of our vegetation is too lush for successful habitation.

Labor Day 2005 trip pausing at the Far Overlook.
The large walnut visible in this photo has been removed and the prairie here is flourishingl

Part of the 2017 field trip group. This year we started and ended at the cabin.

Friday, September 1, 2017

Oak savanna restoration: when should the first burn be done?

When the first oak savanna burns were done at Pleasant Valley Conservancy in 1998 they were unsuccessful. The fire moved a few feet away from the drip torch line and then stopped. At the time we were told that “there aren’t enough oak leaves”, and this is why the fire did not carry.

With extensive experience doing oak savanna burns over the past 19 years, it is now possible to conclude that this explanation was incorrect. Take a look at the forest floor in the pictures of Kathie using a drip torch, both from 1998. There are plenty of oak leaves. After all, this is the first time in over 50 years that this oak savanna had been burned, and leaves had been falling ever since. Because of the slow decomposition rate of oak leaves, there was plenty of fuel, as the second photo especially shows. (Oak leaves are resistant to decomposition because of their high lignin content and rich array of tannins, which slow microbial activity.)

The reason the fire did not carry was because of all the coarse woody debris on the forest floor, and the dense tangle of living shrubs, mostly prickly ash, especially visible in the first photo. The fire movement is blocked by all the woody debris. Also, each standing woody stem blocks the movement of fire, and takes up space on the forest floor that would otherwise have a layer of oak leaves.

Trying to burn  the White Oak Savanna, April 1998. Note all the coarse woody debris and the tangle of brush in the background.
An area of the White Oak Savanna with good oak leaves, but the fire still did not carry well. Same burn as above

So why were we trying to burn?

We had taken our clue from prairie people, who knew that a simple burn could do wonders to rejuvenate a degraded prairie. (Think of the famous Muralt Prarie burn in 1975 in Green County!)

But oak savannas are not prairies. Degraded oak savannas have a heavy legacy of shrubs and coarse woody debris. We should never have burned anyway, because the fire would not get rid of the living shrubs. All it would do was top-kill them, and each plant would resprout from the base and send up new shoots, often a lot of them. Indeed, burning had the potential for doing more harm then good!

What we should have done was to clear the shrub layer (cut and treat with herbicide) and remove all the trees that were fire-sensitive and hence would not have been part of the original oak savanna. This was actually a central goal of the management plan, but the urge to burn was pretty strong. And this is what we did do, starting in these savanna areas in 1999.

Incidentally, the savanna shown in the photos is what we call the White Oak Savanna (Unit 12A/B). The photo shows what this savanna looks like in 2014, after clearing and annual burns for over 10 years. Now, when this savanna is burned, the fire carries very well!

White Oak Savanna in 2014, after over 10 years of annual burns.
These are the same trees that provided oak leaves in 1998.


Saturday, July 29, 2017

Story of a backyard open oak woodland: part 2

This is Part 2 of the saga of how we turned our small backyard from scrawny lawn to lush open oak woodland. Access Part 1 with this link.

Kathie and I live in the Village of Shorewood Hills and the word “wood” in the name is apropos. According to the early history of the village, there were open areas and then there were patches of woods that went back to presettlement times. The native trees are all oaks, mostly white (Quercus alba), although there are also some mature bur oaks (Q. macrocarpa). It’s a great area to live in, and although we have large branches hanging over the roof, so far we haven’t had any roof damage.

I think most gardeners would agree that you can’t get a good lawn if its too shady. After 36 years of mowing a scrawny lawn, and with lots of experience doing restoration work at Pleasant Valley Conservancy, we decided to turn our backyard into an open oak woodland.

Kathie started the conversion in the fall of 2011, so this is now the sixth growing season. The species list below shows 48 species, including 5 State-listed species. Pretty good, considering that the area is about 40 X 66 feet.

The original lawn was killed in the summer of 2011 with glyphosate and by late fall the ground was bare. It was planted with oak woodlands seed mix, and then hand-weeded the following summer. Each year a few new species have been added, and hand weeding continues.

Early summer 2012

Late summer 2017


The table gives the current flora. The only species on the list that might be questioned is the lily, whose identity is uncertain. This came from a former next-door neighbor, who did not like the color!

Latin name
Common name
State-listed
1
Actaea alba
White baneberry
2
Actaea rubra
Red baneberry
3
Adiantum pedatum
Maidenhair fern
4
Agastache nepetoides
Yellow giant hyssop
****
5
Agastache scrophulariaefolia
Purple giant hyssop
6
Anemone virginiana
Woodland thimbleweed
7
Apios americana
Hot peanut
8
Aquilegia canadensis
Wild columbine
9
Arisaema triphyllum
Jack-in-the-pulpit
10
Asarum canadense
Wild ginger
11
Asclepias purpurascens
Purple milkweed
****
12
Aster lateriflorus
Calico aster
13
Aster novae-angliae
New England aster
14
Aster sagittifolius
Arrow-leaved aster
15
Bromus latiglumis
Ear-leaved brome
16
Campanula americana
Tall bellflower
17
Cimicifuga racemosa
Black cohosh
18
Cryptotaenia canadensis
Honewort
19
Elymus riparius
Woodland wild rye
20
Erigeron strigosus
Daisy fleabane
21
Eupatorium purpureum
Purple joe-pye weed
22
Eupatorium sessilifolium
Upland boneset
****
23
Geranium maculatum
Wild geranium
24
Hackelia virginiana
Stickseed
25
Hasteola suaveolens
Sweet Indian plantain
****
26
Hydrophyllum virginianum
Water leaf
27
Impatiens sp.
Jewel weed
28
Lilium spp
Trumpet lily
29
Mertensia virginica
Bluebells
30
Monarda fistulosa
Wild bergamot
31
Napaea dioica
Glade mallow
****
32
Osmorhiza longistylis
Smooth sweet cicely
33
Phlox divericata
Woodland phlox
34
Podophyllum peltatum
May-apple
35
Polygonatum biflorum
Smooth Solomon's seal
36
Prenanthes alba
Lion's foot
37
Ratibida pinnata
Yellow coneflower
38
Rudbeckia hirta
Black-eyed Susan
39
Smilacina racemosa
False Solomon's seal
40
Solidago flexicaulis
Zig-zag goldenrod
41
Solidago speciosa
Showy goldenrod
42
Solidago ulmifolia
Elm-leaved goldenrod
43
Tradescantia ohiensis
Common spiderwort
44
Trillium grandiflorum
Large-flowered trillium
45
Uvularia grandiflora
Bellwort
46
Veronicastrum virginicum
Culver's root
47
Viola soraria
Door-yard violet
48
Zizia aurea
Golden Alexanders