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Tuesday, June 28, 2022

Natural Ways to Kill a Tree

Girdling and Fire 

Stewards and managers of oak ecosystems know their biggest problem is the dark. Too many shrubs and trees. Our oaks and their thousands of interdependent animal and plant species represent more than 5 million years of evolution. These fire-dependent ecosystems comprise our richest wooded lands. But they’re losing species – dying a death of shade.

 

Knee-jerk environmentalism deplores killing any tree. Many well-meaning folks initially resist thinning. Other people argue that cutting trees is indeed natural. Certainly beavers do it. But in this post we’ll focus on two ways biodiversity stewards achieve standing dead trees – girdling and fire. 

 

A Very Short Case Study

One of the finest oak woodlands in northern Illinois was acquired at great expense by a conservation agency. Three decades later a study showed it to have ten times more trees - mostly not oaks. Plant and animal species, starved of light, were dropping out. The preserve was degrading. Occasional mild burns had not been enough for sustainability. Too late now, to solve the problem by fire alone. Time to cut or girdle. 

 

Part the First: Girdling

 

The basic principle behind girdling is simple: remove the phloem and leave the xylem. If you’re like me, you once knew the meaning of those words, but then forgot. The inside of a tree is the wood, the xylem, the stuff a xylophone is made of. Wood is important to a tree, but dead. The phloem is not the bark. It is a half-inch or so of living tissue that surrounds the xylem, and it has a crucial purpose. It brings the products of photosynthesis down from the leaves to nourish the roots. 

 

Most trees, if you cut them down, will put up lots of shoots, from what’s stored in the roots. (The roots send water and minerals up to the branches and leaves through the sapwood, the outer wood, just inside the cambium.) In time, those shoots will grow into new trunks.  But if you girdle most trees, the roots will sense that the top is still doing fine and doesn’t need more shoots. Yet the roots will starve. Is starve too harsh a word? The roots will age peacefully, go through the stages of life, and give up the ghost in tranquility. No one will hear the tree fall, because it will stand for many years as a bounty for woodpeckers, other hole nesters, beetles, and mushrooms. A smooth transition from living to life-giving – how beautiful is that!

 

Few understand either “the why” or “the how” of girdling. But some are learning. Shown here are stewards Monica Gajdel and Charlotte Ahern at Shaw Prairie in Lake County.

 

Th next photo shows the heart of Shaw Prairie, about 100 feet west. The major problem here is encroachment by aspen. With lack of fire, this one tree species can destroy a rare high-quality prairie as the network of tree roots launches an army of thousands of new trunks. Great effort for years had gone into driving the them back, but the roots of the large aspens around the periphery sent reinforcement energy to the dastardly invaders, and they continued to advance.  

When cut and herbicided, these death-dealing little aspens have survived thanks in part to resupply through root connections with the big aspens behind them. 


This post will focus mostly on four sites where Friends of Illinois Nature Preserves girdle for the good. No need for herbicide, quick and easy, safer for the stewards, good for wildlife, good for the ecosystem – girdling is often a best approach. 

 

We stewards and staff spend much of our winters cutting trees down and burning them in bonfires. This too is important and good. But look at the photo below and compute how much work was saved by girdling. Biodiversity loss is a crisis for the planet. Do we have time to waste?

The photo shows a piece of Langham Island Nature Preserve in Kankakee County. This unique island has long been known for incredibly rare plants. Native Americans likely burned it regularly for their own purposes, and a rare ecosystem remnant came along for the ride. Conservationists started to cut and burn in the 1980s. But they didn’t burn enough, and trees and brush grew so dense that most of what was special about the island faded out … or barely hung on. When Friends of Langham Island came on the scene in 2014, their biggest challenge was too much wood. They cut enough in a few key places to demonstrate that rare nature here could recover. So far so good. But, decades after restoration had begun, more than half the island still lay the gloom of unnatural shade. 

Belatedly, we girdled. I count thirty trees girdled in the photo. Compare that number to three trees we saved (bur and white oaks, marked with blue and white flagging). A shocking slaughter? But an oak savanna thrives best with fewer, scattered trees. The rare plants and animals here needed more light. Reproduction of the oaks requires more light. (In other parts of the island we left more shade – or cut all trees to restore prairie. There are many considerations, and variation itself is part of nature.)


One more dramatic fact about the photo above. We had marked those few young oaks years ago. By the time our work reached here, the one in the foreground was already dead. Shade kills. Let there be light. 

  

Let’s review in more detail why girdling may be a good approach:

  • Herbiciding may be needed for many purposes, but we prefer to minimize it in the natural ecosystem. Girdling uses the trees' natural processes to replace herbicide.
  • Especially when there are thousands of invading stems close together, there is a risk that enough herbicide to kill the invaders will kill many of the surrounding grasses and wildflowers also. We worry about that risk most in the finest, rarest areas.
  • In many preserves, old standing dead trees are missing. They're an important part of a natural ecosystem. To thrive for wildlife, woodlands and savannas often need more standing dead trees than they have today. 
  • There is urgency. Most nature preserves don’t have either the budget or staff that they need. They never will. The needs are too great. Bigger budgets, more staff, and more volunteers are needed –  and more efficient methods. It’s not good enough to argue that “we’ll just keep plugging away.” More and more priceless biodiversity is being lost day after day, year after year, decade after decade. Girdling speeds the recovery.
  • It’s safer. You girdle and leave before the limbs and trees fall. In most cases, the tree never does fall. Instead it disassembles: little branches drop first, then fungus rots, and finally, dried out, standing or fallen trunks burn up during a controlled fire. 

While “the old snag” is standing, the ecosystem appreciates the diversity of fungi, bacteria, lichens, grubs that eat wood, and woodpeckers drilling holes. Animals that raise families in those holes include flying squirrels, great crested flycatchers, eastern bluebirds, wood ducks, screech owls, chickadees, titmice, wrens, white-footed mice, all the woodpeckers of course, and much more. 

 

How to

 

It is by far easiest and most successful to girdle during the “period of bark slip” – late spring and early summer. At this time, the cambium is growing fastest, the phloem will pop off with a little help. (The cambium is the thin, weak, creative layer that divides the xylem from the phloem – and which generates both.) 

 

With a saw or axe, make two cuts around the trunk about six inches apart.
Then with a hammer or the back of an axe, knock out the phloem, which may even pop off in one piece if the bark is “slippy” enough. Do not try to shave off the phloem, even though it might seem easier, because it’s then difficult not to leave strips of connecting phloem or cambium, in which case the trunk will recover, and you’ll have wasted your time. 

 

Special cases

 

Aspen is an especially good tree for girdling because any other approach is likely to result in monstrous re-sprouting from far-flung roots, no matter how much herbicide you apply. In my experience, isolated stands of large aspens were entirely killed with no re-sprouting by simple girdling.  If the aspen already have a lot of root sprouts, this approach does not kill them. But it does prevent the large trees from over-riding the herbicide. Someone might also ask: “Why kill aspen at all? It’s a beautiful and native tree.” That’s true. In large preserves it may play an important role in the fire dynamic. But for some remnant savannas and prairies it has become a lethal invader and needs control.

 

Black locust, silver poplar, and tree-of-heaven don’t respond well to girdling. Unlike most trees, for unknown reasons, they put up massive root-sprouts. These species can be better controlled by regular cutting and stump treating, or by frilling, in which you make deep cuts into the tree and apply herbicide. Even then, you may get lots of resprouts, which then will be best controlled by foliar spray.  

 

Buckthorn can be successfully girdled, but it’s rarely worth it. Girdled buckthorns often put up a circle of sprouts under the girdle, which can be knocked off easily, and then the tree dies. But buckthorns are often so dense that all the dead and falling trees make such a mess that it’s hard to facilitate ecosystem recovery, so we cut and burn them. 

 

Follow up

 

In years following the girdling, sometimes no follow up is needed. The tree dies; the limbs gradually fall off; the trunk bit by bit flakes and crumbles; and the remains are just nature. In other cases, the dead tree catches fire during a controlled burn, and it goes out in a blaze of glory. 

 

But dead trees can need clean-up. All trees die, sooner or later, and may become a problem. If a girdled tree presents a danger to a trail or other heavily used area, most managers would cut it before it starts to weaken, as with any dead tree.  

 

If a great many trees girdled at the same time fall and make a colossal mess at the same time, as sometimes happens, at least two approaches are possible. One approach is to cut them all up and burn then in bonfires, as we might have done in the first place. This takes time, but there are still advantages. The dry wood is lighter and burns faster and cleaner. Herbicide expense and damage were avoided. And the woodpeckers and their friends had a great time for years. Another approach is to just let them rot or burn and, in the meantime, explain to horrified people what’s going on.   

 

Part the Last: Kill by Fire

 

Killing big trees with fire takes a hotter burn than most sites get. It’s easy to manage a fire that will top-kill saplings. It’s more difficult to manage a fire powerful enough to kill large invading, over-dense trees. Many burn bosses successfully do it, on rare days when they get the right weather. Over the millions of years that prairie and oak woodland biodiversity evolved, the fires that spread and raged most extensively over the landscape occurred on days too hot, dry, and windy for most fires today. That's why we sometimes have to cut and girdle. 

 

Bonus photos and details

Below, a former landscape of prairie, fen, and sedge meadow had been over time invaded by clumps of box elders, buckthorns, cherries, and the like: 

Friends of Kishwaukee Fen Nature Preserve first made a plan,

 then cut the buckthorns out of the way last winter. 

For the bigger trees, this summer Ben Davies (right) saws parallel cuts through the phloem. 
Next, like Tom Ziomek (left) he'll use a hammer to knock out the sawed strip. 


After quickly girdling the bigger trees in June, the stewards went on to other priorities. During this summer, they are herbiciding the understory buckthorn seedlings and other invasives. This fall, they’ll re-plant the prairie that once grew here, which is expected to start off well in 2023 under a “nurse crop” of thinning trees. When the trees are dead and dried, they'll be burned on some cold winter day. Standing dead trees in a prairie are not a plus. 

 

Notice above that some girdles are bright, and some are dark. The fresh girdles stand out shockingly (or “beautifully,” according to some). Trees girdled a week earlier have turned darker. 

 


At least five elements stand out in the above bonus photo from Langham. 1) To the left rear, you can see how dense the honeysuckle and other brush had been. 2) To the right rear, you can see the one old oak that grew in an open habitat. 3) All the others are “pole trees” which will never make a natural ecosystem here. If you blow up this photo, you can see four small bur or white oaks marked with blue-and-white flagging; they’re much smaller than the pole trees and would have died soon without help from stewards. Some oaks flagged a few years earlier died before cutting or girdling liberated them. The surviving oaks are unnaturally tall, thin, and weak. Opening up this area by girdling gives them a better chance to grow stronger trunks and broader limbs, as such oaks normally would. But if they start to break or fall over, we may cut the tops (above deer-browse level) and let them fill out as would be more natural for an oak. 4) Some understory grasses and wildflowers have begun to recover; mostly they are woodland plants that have invaded during the time of shade; other species are being seeded in from more open parts of the island; a few species are recovering from the fire-liberated seed bank (but they won't survive if it's too dark). This more gradual process may lessen the chance that aggressive species like tall goldenrod will take over. 5) Stewards Molly Bilderback-Ulrich and her sister Ally can do this powerful work efficiently … while others pull invasive weeds and gather seeds. They found that 3 people could girdle 23 trees in 2 hours.   

 

On a great  2018 tour of Braidwood Savanna, Will County Forest Preserves’ land manager Floyd Catchpole showed us the above sedge meadow. It had been degrading in the shade of invading silver maples. Staff not only girdled the maples shown above but also many over-dense oaks in the sand savanna visible behind the meadow. 

 

Pole sugar maples girdled among bur and white oaks in Somme Woods. Note the almost complete lack of  grasses and wildflowers.

 

Young but big cottonwoods around a pond that had been in an open savanna landscape in a 1938 aerial Somme Woods photo. These were girdled by staff with chainsaws.

 

The options and decisions can get complicated. Consider this Somme Prairie Grove photo: 

Should this beautiful shagbark hickory have been “a keeper” or “a girdler”? Trees are far apart here, and shagbark is a natural part of an oak woodland. It would not be unreasonable to retain this tree and let the fires decide if it should go. In high fuel areas, hot controlled burns often kill hickories. But this area is receiving intensive restoration. Sadly, the original vegetation at this spot was killed utterly by dense shade, cleared years before. Restoration depends on painstakingly gathered rare seed. We don’t want to waste it. The 1839 Public Land Survey shows this area to be on the line between prairie to the west and savanna to the east. Thus, any conservative surviving fungi, invertebrates, bacteria etc. would be adapted to prairie or savanna - not woodland. 

 

The above photo looks east. The girdled hickory and the bigger red oak next to it are relatively young trees here. The two trees in the background tell the real story. They have huge horizontal limbs reaching west. They stood at the western edge of trees here; the hickory stands in former prairie. The next photo will show our same hickory, but looking west. 

In this direction, all was prairie. Those tall, thin trees grew that way among others in the absence of fire (most since cleared by stewards). They are not adapted to the biodiversity restoration under way here. They've been left in place for now because there were higher priorities. Perhaps over the years and decades they’ll remain and develop an okay relationship with the gradually improving prairie and savanna around them. Perhaps not. We don’t have extra time to think and plan for them at the moment. But this foreground tree was adjacent to an area of recovering high quality savanna. Fuller light was needed. As the hickory dies, we will scythe the dense woodland sunflower and tall goldenrod around it, to save many semi-smothered species that are struggling to gain a toehold. (They include wide-leaved panic grass, yellow pimpernel, baneberry, and rue anemone to the savanna east – and Leiberg’s panic grass, cowbane, Canada milkvetch, and Culver’s root of the savanna-edge prairie to the west.)   

As stewards watch results and adjust the plan (as the ongoing process here is beyond detailed predictions), we may work to facilitate prairie in this spot (no shade) or savanna (some shade). The decision may depend in part on whether especially significant species here seem to need more of one habitat or the other. As the world turns. But we’ll be inspired to do our best by the success of older restoration on the back side of the low glacial hill you see on the right. There, young bur oaks thrive among very high-quality herb vegetation. Thus, two last photos, the first taken on the other side of that low hill, in an area of restored high quality, looking west:

 

Second, a photo taken on this side of that hill, on the edge of the bur oak woodland:

This was all bare ground under buckthorn. The herb flora restoration started "from scratch." All that was here were the old oaks, the soil biota, and some invertebrates. 

None of the herb species identifiable in in the above two photos were in this area when the restoration began. Such recovery of ecosystem health is what inspires us stewards.  

 

Bonus eight-second video


Okay, it's goofy, but fun, and what we managed to record. Emma Leavens asks a significant question: Instead of whacking off the phloem, she tries pulling it off, and she asks Molly if that's okay. 


Molly assures her that it is. Technically, it's "shaving" the phloem off that tends not to work. When people try that, filaments tend to survive through which the phloem can grow back; a year later you'll have a whole new phloem, and the problem shade will stay the same. What you want is a clean break at the weak cambium layer. That's why it's generally best to whack it during the period of bark slip ... so it pops off or peels away. 


Bonus diagrams and a sort of a cartoon 

old drawings by S. Packard 

from a 1991 Nature Conservancy stewards handbook




Additional info on the sites


Kishwaukee Fen Nature Preserve:

https://woodsandprairie.blogspot.com/2021/09/introducing-fen-in-need.html


https://woodsandprairie.blogspot.com/2021/10/kish-fen-kick-off-sunday-oct-17.html


https://woodsandprairie.blogspot.com/2022/03/controlled-burn-at-kishwaukee-fen-march.html


Langham Island (Kankakee River Nature Preserve):

https://woodsandprairie.blogspot.com/2014/08/survivor-langham-island.html


https://woodsandprairie.blogspot.com/2014/10/myth-or-miracle-unexpected-news-of.html


https://woodsandprairie.blogspot.com/2019/10/degradation-and-redemption-at-langham.html


https://woodsandprairie.blogspot.com/2020/08/langham-island-rebirth-of-rebirth.html


https://woodsandprairie.blogspot.com/2020/09/september-12th-langham-island-update.html


https://woodsandprairie.blogspot.com/2020/11/langham-island-update-and-plans-nov-5.html


Shaw Woods and Prairie (Skokie River Nature Preserve):

https://woodsandprairie.blogspot.com/2021/09/the-diversity-and-promise-of-shaw-woods.html


https://woodsandprairie.blogspot.com/2021/11/anatomy-of-new-community.html


https://woodsandprairie.blogspot.com/2022/03/burn-at-shaw-prairie-march-21-2022.html


https://woodsandprairie.blogspot.com/2022/05/may-14-2022-shaw-woods-what-we-did-and.html


The Somme Preserves:


Somme Prairie Grove

https://woodsandprairie.blogspot.com/2017/07/july-9-2017-restoration-tour-of-somme.html


https://woodsandprairie.blogspot.com/2018/02/the-somme-prairie-grove-experiment.html


https://woodsandprairie.blogspot.com/2020/10/a-celebration-of-vestal-grove-study.html

 

Somme Woods

https://woodsandprairie.blogspot.com/2017/12/the-unexpected-discovery-of-somme-woods.html


https://woodsandprairie.blogspot.com/2018/02/principles-of-somme-woods-conservation.html


https://woodsandprairie.blogspot.com/2018/04/breeding-bird-revival-after-habitat.html


Acknowledgements


Fundamental credit goes to the stewards and staff and interested supporters of the land-owning and conservation agencies:


All sites - Illinois Nature Preserves Commission

All sites - Friends of Illinois Nature Preserves

Braidwood Dunes - Will County Forest Preserves

Kishwaukee Fen - Village of Lakewood

Langham Island - Illinois Department of Natural Resources

Shaw Woods and Prairie - Lake Forest Open Lands Association

Somme Preserves - Cook County Forest Preserves


Girdling diagram by Paul Nelson from the Tallgrass Restoration Handbook (Packard and Mutel, eds.) 


Credit for proofing and editing go to Rebeccah Hartz, Jess Sladek, Eriko Kojima, Andrew Rosulek and Molly Bilderback-Ulrich.

10 comments:

  1. For stewards, killing trees is not the end of the work, it is the beginning.

    While soil organisms are moving into the dead tree and consuming it, they are using available soil nitrogen. There is a short window of a few years when very little is growing which gives an opportunity to get low-nitrogen competitive species established. I have not always been good about utilizing this opportunity. Invasive species tend to fill in if this opportunity is not seized, like crown vetch when present, reed canary grass, or tall goldenrod. If invasive species that will take advantage of sunny open ground are present, then control should occur before killing trees. A native plant that grows after trees have been killed is Erechtites hieracifolia. However, this species is soon overtaken by tougher native species.

    Leaving fallen trees to decompose creates opportunities for different vegetation and heterogeneity. When large oaks fall over, sedges and ferns grown on the north side of the log. Near water, fallen wood is colonized by sedges and/or woodland wildflowers. I believe the diversity of ants that Laura Rericha-Anchor found at Timber Hill in Iowa is likely was because all cut wood was left to decompose rather than merely the frequent prescribed burn interval. Ants love to nest in dead wood and some farm fungi as food.

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  2. I won’t cut and pile buckthorn or anything else anymore. It is too physically demanding. Two hours of hauling and burning wood and I am exhausted for a few days. In contrast, if rain is not expected for several days, I can use a mini-paint roller to apply Garlon 4 in basal oil to the bark. If rain is expected I can apply glyphosate to frills on larger trees. I can do these activities for 6 hours during day without completely exhausting myself. Girdling is probably better than applying herbicide to frills in some situations, but I don’t like to work harder than necessary and find the later easier. I infrequently see impact to adjacent vegetation when applying glyphosate to frills and in these cases, it is black raspberry or gray dogwood which are already over abundant.

    I leave buckthorn, bush honeysuckle, and larger trees standing. The small ones fall over a few years later and aren’t visible under the vegetation as they slowly decompose. Some of the large buckthorns fall over after several years. I don’t see large dead buckthorn that has fallen over as a mess. I see it as cover for rabbits that eat the over abundant black raspberries all winter. It also deters deer browse in the location where the buckthorn has fallen creating some heterogeneity in vegetation. Cottonwoods snap off and fall over. Black cherries and oaks with hard wood often stay standing as the woodpeckers disassemble them piece by piece.

    I don’t spray the flush of buckthorn seedlings after larger buckthorn have been killed. I have seen yellow star grass, violet wood sorrel, golden Alexanders, purple meadow rue, sedges, nanny berry, and wild rose survive in sparse numbers under common buckthorn for over a decade. In November, I run my mini-paint roller across the top of large patches of buckthorn seedlings to apply the minimum amount of Garlon 4 in basal oil to kill them. I am careful to avoid wild rose which would be killed if touched by this herbicide. During this time, I also follow up in areas where buckthorn had been treated earlier to treat small buckthorn sapling. I prefer controlling the buckthorn by attrition rather than killing everything by spraying an area then rebuilding from scratch with seeding. My observation is that spraying tends to favor the invasive or aggressive plants whose seedling can best tolerated the residual herbicide.

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    Replies
    1. James, I appreciate your thoughtful comments. It's good that many people in many places are experimenting with various approaches. My experiences in places I've worked often differ from yours. Understandably. Great, careful pains may be taken in small areas using techniques that we don't yet have the resources to employ in larger areas. Experiments can help us increase efficiency and build capacity. Many people are doing admirable work. It would be great if we could develop more and better ways we could all learn from each other.

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    2. “All things are poison, and nothing is without poison; the dosage alone makes it so a thing is not a poison.”

      Paracelsus

      Yes, experiences differ especially as it relates to herbicide. If too little herbicide is applied, time and effort is wasted. If too much is applied, and/or best techniques are not used, then other things are killed. Too much herbicide also delays an ecosystems recovery. My observation is that unselective applications of herbicide, like any type of foliar spraying, selects for the most robust competitors which are the aggressive/invasive species we don’t want. Hence, the tendency to kill everything and start over.

      I wish scientists studying ecological restoration did a better job comparing techniques. There are lots of papers recording the results but few that compared different techniques.

      I should mention I only apply Garlon 4 in basal oil during the dormant season. I have found that even if it is applied carefully, the vapors impact adjacent vegetation. I have marked some of this vapor impacted vegetation after a careful application during the growing season. The vapor impacted vegetation did not return the following year.

      I also neglected to mention that I take care to avoid nannyberry when rolling my herbicide laden mini-paint roller over abundant buckthorn seedlings. I now mark any nannyberry I find in a planned treatment area during the summer before an application. I have so far unintentionally killed two nannyberry bushes while treating the multitude of buckthorn sapling. I am taking a more proactive approach, so they are highly visible and easier to avoid.

      I commend you for using girdling. Sometimes what the ecosystems needs is not popular. People don’t like seeing dead trees. However, I think this is the best method to accomplish your conservation objectives.

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    3. MIDSTORY HARDWOOD SPECIES RESPOND DIFFERENTLY TO CHAINSAW GIRDLE METHOD AND HERBICIDE TREATMENT

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    4. Yes, you caught me. I was using broad statements to keep my comment from being too long.

      The species I currently control in approximate order of decreasing frequency in historic prairie ecosystems are common buckthorn, bush honeysuckle, multiflora rose, white mulberry, some box elder, red elm, European high bush cranberry, green ash, honey locust and occasionally a few black cherries. I have not worked on sugar maple recently. I have not tried girdling on this species since the county preserves where I live did not allow it when I was previously helping doing work in a woodland area. My observation with sugar maple has been fire tends to kill them slowly by girdling the stem if they are less than ~4 inches diameter at breast height.

      I apply triclopyr ester in oil to lots of common buckthorn, bush honeysuckle, multiflora rose, small red elm, European high bush cranberry, small green ash, and small to medium size honey locust.

      I apply glyphosate to cuts around the stem, called frilling, to buckthorn if rain is forecasted within several days, any white mulberries, and to the box elders that I decide to control. I vary the concentration of herbicide I use for each species and in cases where the herbicide must be applied to cuts made higher on the stem. Cuts often must be made higher on the stem when I make them in the center of multi-stem buckthorn.

      I use applying herbicide to cuts made around the stem just above ground level as a replacement for hot fire. Extremely hot fire would kill many of these woody species down the stem far enough that they would not produce basal sprout and would be killed. In the absence of extremely hot fire, the herbicide acts similarly by killing the tissue down the stem of these species just far enough that the woody plant will not sprout and will be killed. I try to only use enough herbicide to kill tissue far enough down the stem that sprouting does not occur, but not to the point that adjacent plants are impacted. It is a delicate balance, but necessary to preserve ecosystems created by wildfire when for obvious reasons extreme fire is not always a possibility.

      Additionally, I like applying herbicides to cuts around the stems made low to the ground for aesthetic reasons. When I make cuts low to the ground, they are not visible when vegetation fills into the area. Once the bark has fallen off the decaying woody plant, the cuts are barely visible at all. This makes it look as if a tree has died of natural causes. I prefer this to double girdling where cuts into the wood are visible until the tree has mostly decomposed.

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    5. I should mention a few more thing about applying glyphosate to cuts into the bark around the stem, also called frilling.

      My trials have repeatedly shown that applying herbicide to cuts into the bark around the stem is more effective, even when a lower concentration of herbicide is applied, than cut stump treatment. When the herbicide is put into cuts into the bark around the stem, rather than on a cut stump, the herbicide does not get splashed onto adjacent plants when rain occurs. Unlike cut stump treatment, I never see damage from rain splashing herbicide onto adjacent vegetation when herbicide is applied to cuts into the bark around the stems. Although, herbicide being transferred through root connections is still a concern.

      When applying herbicide to cuts into the bark around the stem, the stem is not cut. Since the stem is not cut, apical dominance has not been broken. If the plant is not killed during the initial treatment, the plant does not sprout from the base. When herbicide applied to cut stumps fails, the stumps sprout. These sprouts are then typically foliar sprayed which often heavily impacts and nearby plants. Applying herbicide to cuts around the stems avoids this damage.

      More information can be found at the following link.

      https://grasslandrestorationnetwork.org/2018/02/18/cut-stem-treatment-on-buckthorn/

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  3. I should also mention that I trial herbicides on a small scale to determine minimum concentrations and amounts that are effective. Using the minimum amount of herbicide to accomplish a job applied in a strategic manner is how I avoid damage to adjacent vegetation. See the below video for impacts that can occur from herbicide applied carelessly.

    https://www.youtube.com/watch?v=pCMN_93-hFw

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  4. My main interest in the following article is the 100% kill rate with a single chainsaw girdle and no chemical on sugar maple. Google this;

    MIDSTORY HARDWOOD SPECIES RESPOND DIFFERENTLY TO CHAINSAW GIRDLE METHOD AND HERBICIDE TREATMENT

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  5. “But buckthorns are often so dense that all the dead and falling trees make such a mess that it’s hard to facilitate ecosystem recovery, so we cut and burn them.”

    My experience with the above has differed with Mr. Packard’s. A lot of the small buckthorns that grow tall and skinny under a canopy of other trees, or other buckthorns, do fall over about three years after treatment. They become so brittle that when you step on them, they shatter and make little to no difficulty accessing an area. Walking through an area quickly turns these buckthorns into a wood mulch.

    A few of the larger buckthorns do fall over too. However, several years after treatment most larger buckthorns that had been controlled in dense thickets are still standing. Even in death, the density of buckthorns in thickets continues to help support each other preventing most of them from falling over. Under the dead buckthorns, Impatiens capensis has developed in moist calcareous habitat that was previously prairie. Over time, I hope longer lived species will move in to take the place of this annual that I admire. In drier areas, some prairie plants have survived under the buckthorns. However, a lot of weeds take advantage of the bare ground and the worst of them will likely need to be removed/controlled until long lived competitive native species have occupied the space.

    To access areas within thickets of buckthorns, live or dead, I carry a pair of pruners that I stick in the small pocket of my jeans. Cutting away small branches is all I’ve found to be necessary to access an area so I can complete my work. Not cutting and burning wood allows me to control many times the number of buckthorns, or other woody invasive species, accomplishing more for a greater benefit to the native species.

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