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Friday, January 26, 2024

Destructive Herbicide in the Ecosystem

Course Correction: From being “Invasives Killers” to “Biodiversity Conservationists”

 

Wake-up Call

The best conservation land management works well and is profoundly important. But we conservation land managers also have to look at the parts that need fixing. What passes for our work can be wasteful, destructive, and incompetent. 

 

We staff and volunteers want our work to be successful. On paper, it looks good for hard-working agency staff to secure grant funds, have contractors work on X number of acres, and put that in a report, as if that's a sufficient measurable accomplishment. But such measures – of dollars spent, acres covered, and percent successful invasives controlled – leave out what’s most important. How much did the long-term integrity or health of the ecosystem improve, or deteriorate?

 

Most of us want to be positive as much as possible – especially when the challenges are so great and the resources so small. But that’s also why it’s important not to waste. The five stories below are true and more common that we wish. We need to think about how to do better. Sites aren’t identified, mostly so the facts can be presented forthrightly, without antagonizing the good people in charge, who are doing their best in most cases.

 

This post is not an “anti herbicide” protest. Wise use of herbicide in biodiversity conservation is utterly essential. Above, buckthorn, which has been re-sprouting here after every fire for decades, has been sprayed efficiently in fall, after most other species have gone dormant. The herbicide, recognized by blue dye, is clearly also damaging some desirable species. There’s often no practical way to avoid some losses. But the adjacent species will quickly fill in where the buckthorn died. It would be possible here to avoid killing any other plant, and some perfectionists feel great angst over this kind of thing. But if we followed their advice, we’d use up too much time, and a great deal of other dearly-needed work would not get done.   

 

Five Examples of Dismal Failure

 

1. Complete death of very high-quality prairie

 

A Grade A (very-high quality) mesic black-soil prairie was deteriorating from brush, mostly gray dogwood. Diverse prairie survived under the dogwood, but diminishingly. Professionals (from a contractor with a rep for taking extra care) painted the stems with the herbicide Garlon in winter. The whole prairie died in the areas where they worked. Next summer the ground was bare, except for small re-sprouts of the dogwood, which had the most vigorous root system. Despite covering a small part of the prairie, the death of a substantial patch of Grade A was a profound tragedy. 


This heartbreak baffled many experts, who evaluated after the fact. Many people assured us that they had done “this kind of thing” without the negative impact. But was it really the same? How carefully had they studied the prairie vegetation before and after? How similar was the weather? How similar were the volumes of herbicide applied? We wish we knew. Many of us are doing more experiments to learn what we can. Fortunately, in a way, few people need to worry about impacts on Grade A prairie, because there’s so little of it. Unfortunately, saving Grade A areas is a highest priority. Do we have insufficient knowledge to do it right? 


Dense stems had been cut and painted in a different, poorer quality area nearby. In that area too, the prairie died, as shown below. 

On the upper left, the dogwood was not cut or herbicided. 

On the lower right it was. But the remnant prairie died. 

For more detail on this incident, click here


2. High-Quality Woodland Loses Diversity from repeated Reed-Canary Mistakes

 

A rich woodland had patches of invasive reed-canary grass here and there. Contractors seem to have recognized the quality of the intermixed herb vegetation and carefully sprayed only that invasive grass. Instead of a grass-specific herbicide, they used Round-up, an herbicide that kills most plants. While they eliminated the reed-canary in the centers of the patches, they failed to spray the reed canary at the perimeter of the patches, which was hidden beneath the quality vegetation. Perhaps they were unable to see it underneath the good plants, as they worked quickly to spray the many patches in the contract area. But the result was that the dead zones where the Round-up had killed the remnant vegetation grew larger and larger over the years. 


A better approach is to carefully and assertively spray the reed canary at the leading edge of the infestation, even at the cost of collateral damage, in order to eliminate the patch once and for all. The staff people in charge said they hadn’t had enough time for more detailed monitoring. It was as bad a loss as if those areas had been plowed … or had a Burger King built on them. We have to do better. 

 

3. Foliar Spray in Good Quality Woodland Kills All – Even the Old Oaks

 

Here’s another case when the supervisors were stumped. How could this happen? 

 

In an oak woods of hundreds of acres, the volunteer stewards made slow progress on invasive brush. Contractors were hired to help out and demonstrate effectiveness on two acres. They cut adult buckthorns and sprayed the dense seedlings. On paper, for the short term, the results looked excellent. Dense patches of seedling and sapling buckthorns were entirely dead. You could walk around the distinct edge of the two sprayed acres and see a sharp line between where buckthorn in the treatment area was brown and dead – and the adjacent area was green with young buckthorn. But by the end of the summer, all the trees had died too. Some were old bur and white oaks, many feet in circumference. 

 

I asked questions about it but didn’t want to push too hard, so as to maintain a good relationship with the owning agency. Staff explained, “Perhaps they put a brush pile in the wrong area.” Clearly they hadn’t looked carefully – or even paid much attention to what happened.

 

A year later, I asked the contractor if they ever figured out what the problem had been. The fellow was surprised by the question. Staff had never asked them about it, and the contractor hadn’t been back to check. He claimed not to know what herbicide his company had used. People clearly hoped the problem would just go away. (See Endnotes 1 and 2 for some expert opinion on what had happened).  

 

At that point, I wondered if I’d made a mistake by not saying more at the time. I’d worried about provoking a backlash that might have had negative impacts on that agency’s overall program. But we need to understand this stuff. And by “we” – I mean to include volunteer stewards and advocates, who can be more willing to say that ‘the Emperor has no clothes’ when needed. Especially at this stage of knowledge, just leaving the evaluations to  overworked staff is not good enough. 

 

4. White-fringed Orchid vs. Canada Thistle

 

The Federal-endangered prairie white-fringed orchid (Platanthera leucophaea) can grow in very high-quality grasslands and sometimes in degraded ones – but very few of them grow anywhere. Last year’s census by the U.S. Fish & Wildlife Service found only 223 plants. It’s a truly rare species.

 

One degraded prairie had scores to hundreds of them blooming every year. Then, saw-tooth sunflower over-ran parts of the orchid’s habitat and mostly eliminated it. We scythed the sunflower for a few years – hoping that this treatment would help quality vegetation recover. Gradually, the orchids returned in good numbers, and other quality vegetation like smooth phlox and yellow stargrass increased. Another problem – the invasive alien, Canada thistle, was a minor presence. A contractor working in a nearby area sprayed it, despite being  asked not to do. Thinking that they knew better, they sprayed it, rather aggressively, with Round-up. The recovering prairie was badly set back. Many aggressive species began shading out the more conservative ones. In recent years, other aggressive species dominated, and few orchids bloomed there.  

 

5. Mighty Mowers followed by Massive Broadcast Spray

There are ferocious machines that can mow mature buckthorn and other brush and turn it into inches-deep “slash.” Top-killed brush resprouts the following spring, and broadcast spraying can control it. This approach can be very helpful for restoring large areas under some conditions.


Dense buckthorn can be controlled by mighty machines followed by heavy herbiciding (as shown above) or by “basal-barking” (as in Dismal Failure example 1.) 

 

What happens in oak woodlands that retained areas of remnant biota? We’ve seen this treatment wipe it out, including endangered species, and very probably much of the symbiotic soil biota as well. 

 

Perhaps a standard practice in such areas should be to set aside some of the best remnant patches for more discriminating approaches. Then the biota of these areas could spread through the rest of the woodland over time. 

 

Comparing Two Approaches 

 

Consider crown vetch, an invasive that can wipe out large areas of good prairie or savanna:

 

Approach 1. We know sites where people have been spraying “the same” crown vetch for decades. It just doesn’t go away. They complain loudly and cynically, but it’s their own fault. 

 

Their strategy? They go after the worst areas first, where they can kill the most with the least effort. Their work becomes endless whack-a-mole.

 

Approach 2. We know sites where crown vetch control was successful. That is, it’s now gone. What was the difference? 

 

The successful folks start with the smaller patches in the highest quality areas and eliminate them. They GPS or mark them on the ground and return every summer for a few years to give the final spritzing to any re-sprouts or seedlings. They search diligently around the former patch edges, as that’s where the vetch will most likely be holding on. In higher-quality areas they use one of the newer herbicides that are somewhat selective about which types of plants they control. Bit by bit, as time and resources permit, they go after the bigger patches in the poorer quality areas until those too are gone. 

 

Who’s In Charge Here?

 

All the concerns implied above are potential problems whether staff, volunteers, or contractors are doing the work. When, instead of a contractor, a staff person does the work, the person who evaluates results is typically that staff person. Given levels of resources, perhaps there’s no alternative. Most academic research doesn’t help with these questions. We need more practical, applied, insightful research by people who understand this field. 

 

At some sites, expert volunteers do the most sensitive and demanding work – often taking more delicate care than it would be possible to pay contractors to do, given current budgets. Some volunteer stewards take time to study the results of extra-detailed care and write up results. At some sites staff do excellent studies and learn from each other. Perhaps there should be some sort of clearinghouse where we all could record what we’ve learned, especially as it concerns the varied approaches that work best according to different soils, ecosystem qualities, weather conditions, etc.? And some knowledgeable editor could make the info easily accessible to practical on-the-ground folks.  

 

There are also broader problems that need discussion, study, and more-detailed best management practices. Remnants and all higher-quality areas need different practices and types of oversight than badly degraded sites. Perhaps a new profession is needed, sort of a “general practice doctor” for the ecosystem, who can recognize needs and recommend expert practitioners. That person wouldn’t mostly do the work but instead would evaluate, prescribe, review, and revise. People with such expertise would likely come from the ranks of on-the-ground restoration practitioners with extensive experience.    


Is killing invasives our goal? Or restoring integrity and health to the ecosystem? Herbicides are needed. But herbicide treatments may solve one problem while ultimately not helping, or even making things worse. Restoration requires a wise overall plan with appropriate sequencing. The work then needs close oversight by someone who has a good working knowledge of the site’s ecology and the long-range impact of possible treatments.

There are too few people capable of providing expert supervision and review. We’re not learning as fast as we could. Contractors (some dedicated and competent, some not) are often hired on the basis of the lowest bid, and no one has time to carefully evaluate the results. Or someone checks only whether target plants died – with little attention to negative impacts. The highest concern in remnants should be for the remnant species.

 

Endnotes

 

Endnote 1. Imazapyr

Dan Carter wrote: Do you know what herbicide they used? This is a common error made with an herbicide called Imazapyr. Milwaukee County Parks staff killed a bunch of trees at Wehr Nature Center by spraying lesser celandine with it. 

 

Endnote 2. What happened to those old oaks?

Another peer reviewer wrote: Since the buckthorn seedlings were densely packed, the same thing may have happened as with the dogwood clones above: too much highly concentrated herbicide migrating in soil directly or with the help of underground fungus, killing oaks by the root.  Herbicide labels have a “maximum use rate” given in amount of herbicide product applied per acre per year.  That is not the same as the maximum rate to control a given weed, which is stated elsewhere in the label.  Max use rates may be related to such failures as this one.  Or did root grafting occur between oaks & buckthorn?  As Dan Carter has said, the decision to use basal bark or foliar when desirable vegetation is present above or below ground is rarely a good idea.  Basal bark may work in such situations with a meticulous applicator & flawless technique, but such people are so rare it doesn’t warrant recommending that practice in general.

 

Acknowledgements

Thanks for helpful suggestions from Dan Carter, Christos Economou, Eriko Kojima, and two anonymous reviewers. This post also benefitted from written exchanges among Don Osmond, Dennis Nyberg, Dan Carter, and others as found here and here:



 



21 comments:

  1. More detailed herbicide records would help identify the root cause of failures & provide guidance for successful applications. That includes application date, snow/ice conditions, precip records for a week after application, application method (sponge, spray, roller, etc), brand name of carrier & estimate of gallons/acre of herbicide solution.

    The 2nd picture shows a straight kill line despite dogwood stems being unevenly spaced from that line. If herbicide was transported by snow or underground roots, I’d expect an uneven kill line. A picture in your 8/28/20 post on this subject shows only patchy kill in more scattered dogwood that was basal barked. If spray was used for both basal bark & cut stump, the straight kill line is consistent with broadcast spraying when dogwood was dense & spot spraying when it was more scattered. Herbicide at this high a concentration could take a long time to degrade enough to be harmless & if the ground thawed in the meantime, oil based herbicide would soak into the soil & kill natives by the root. This is also consistent with comments in the 2020 blog that imply very targeted spot applications don’t have this problem. Perhaps the species that survived had deeper roots.

    Herbicide licensing study guides don’t teach mindset. Applicators can be taught to recite this mantra before work begins: Soil is not just dirt. It’s a complex collection of living organisms & our job is to protect all life from harm as much as possible, except for the targeted species.

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    1. Thanks, anonymous, for good thoughts.

      Yes, the officially required herbicide licensing test fails to emphasize what's most important because it's designed for agriculture and ChemLawn-type landscaping professionals, who use herbicide by the truckload. Our goals and concerns in ecosystem restoration are so different. The whole training and certifying system should be revamped.

      Thanks for drawing attention to the second photo. I changed the language there to clarify (and added a link to the post you cite). That very straight line in the photo does look suspicious, but I'm fairly confident that vegetation was not sprayed there. The killed area was perhaps ten feet by ten feet, and the edges were fairly sharp, but not as sharp as in this photo, all the way around. Perhaps that photo is not representative but got used mostly because it showed herbicide death so clearly. I'll try to find better photos.

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  2. The problem is herbicide labels are written for people maintaining right of ways, pastures, timber plantations, or farms. By law, herbicide applicators must follow the label. However, if they follow the application techniques described on the herbicide labels, as written, they are going to kill A LOT of off-target vegetation and impact recovery potential. What comes back in the dead zones are tougher invasive plants.

    What is needed is to teach people how to evaluate herbicide applications and techniques. Starting is as simple as tying surveyor’s tape to plants before treatment (or Bill Kleiman will tell you to spray them with tree paint or use metal tags). If treating herbaceous plants, return a few weeks later. If treating invasive woody species in fall/winter, return the following growing season. Take photos of the off-target damage. Return the year after treatment and take photos to document if the impacted native plants were killed or if they recovered.

    Right now, even the best people only have a vague idea of how much herbicide to apply. The label for Garlon 4 (and generic brands) say to cover 12 to 18 inches of stem length when doing a basal bark application. That is about right for the maximum stem diameter the label says can be treated. What length of stem coverage is necessary for smaller stems down to carpets of buckthorn seedlings that are only a few inches tall?

    Herbicide applicators need a table they can take with them in the field. This will allow them to estimate how much herbicide needs to be applied to varied sizes, and shapes, of woody invasive species.

    Applying herbicide is not about extreme precision. Rather, what is important is to have a general idea of amounts so grossly too much herbicide is not applied or so little that the work must all be done again.

    There are statistical methods that can determine how much herbicide needs to be applied under varying conditions by doing a mathematically determined minimal number of treatments. My observation has been the following conditions cause variation in the amount of herbicide that needs to be applied to get a desired level of control when using a specific technique.

    1. Size of the invasive species
    2. Region
    3. Sunny or shaded habitat
    4. Date

    The below post has more discussion on herbicide techniques.

    https://woodsandprairie.blogspot.com/2023/08/bringing-your-game-to-herbiciding.html

    My experience has been that if I do not get glyphosate on a non-target plants when I hand apply glyphosate foam to stems near the ground then the non-target plants will show damage but recover the next year. I have subsequently observed native plants grow much better after invasive plants have been eliminated by a careful application of the minimum necessary amount of herbicide.

    The previously mentioned technique is great for controlling reed canary grass, leafy spurge, purple loosestrife and crown vetch without killing adjacent plants. Coating several inches of stem at the base of the plant with a high enough concentration of glyphosate foam in fall does the job. Although, I will probably find cutting stems (a scythe would work for reed canary grass) and applying herbicide to the cut will be easier for some species, use less herbicide, and reduce off-target damage with more trials.

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    1. Thanks for good comments. I agree that herbiciding does not require extreme precision. We do need better research and better "best management practices" - which do require precision and careful record keeping. But most herbiciding doesn't need any more precision than mowing a lawn, charging a battery, or baking a cake. You mostly just need to follow simple procedures, with reasonable care.

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  3. The link to the prairie case has a comment about successful use of very frequent fire (more often than every three years). We need to do more of that. The enemies of the sod are shade and thatch, and if we can prevent those from degrading it, we'll make process. Growing season cutting to initially get more light in and more sod growth in conjunction with near annual dormant burning holds promise, I think. We need to study that! Multiple growing season cutting seems to be very effective on sumac.

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    1. Wise words. More frequent fire. Growing season cutting of invasive shrubs. Species may respond differently according to weather, soils, associated species, etc. I have experience with cutting a large sumac clone in mid-summer, using no herbicide, and having none come back at all. Ever. The trunks were all old.

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    2. I saw an example where that worked with two cuts on a young clone on a bluff prairie...undetectable the next year. With sumac, it seems an early summer cutting followed by another several weeks later on sprouts is just as effective as herbicide use, which typically requires going back to follow up too (and maybe like your instance with the over-mature clone, just one cut). I'm using multiple growing season cutting on small aspen shoots while girdling on parent trees. We'll see how that goes. I want to experiment on gray dogwood too. I'm still treating that one. Many other problem species absolutely require herbicide treatment and I can't see that changing, but I think if we shift our view towards promoting a "strong sod" we'll be using less, wasting less, and avoiding mistakes.

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  4. From Will Overbeck via Facebook:
    Ok - I have so many bad herbicide stories I don't really know where to start but how about spraying the same patch of Canada thistle about 5 years (or more) in a row before I realized it is better to use native species to out compete that species than to spray away. Integrated pest management.

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  5. From Chris Matson via Facebook:
    Using certain herbicides should require specialized training to learn of the limits and effects, and important cautions that cannot be overstated. Imazapyr, imazapic, hexazinone, the pyralids and others should only be handled with experience or restrained mentorship after the training.

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  6. From Dennis Dreher via Facebook:
    It seems that some (many?) use backpack sprayers for basal barking, and for treating cut stumps for that matter. Inevitably, a lot of herbicide may land on the soil or adjacent vegetation with this approach vs. careful "brushing" of herbicide.

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    1. From Kathleen Soler via Facebook:
      The right thing to do as a land manager is eschew herbicide and use the time and money on community engagement, training and outreach. So many people, particularly people who are well-versed in local ecology, are alienated by herbicide use. I am wary of bringing my toddler along with me to most managed natural areas in the summer. Absolutely certain I'm not alone in that.

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    2. From Dennis Dreher via Facebook:
      Like it or not, it simply isn't possible to do restoration work without the careful, targeted use of herbicide. Without it, much of the natural landscape in this region would revert to buckthorn, reed canary grass, and other invasives. And contrary to the sad issues identified in this post, there are numerous sites that have been safely restored with the resultant return of a diversity of butterflies, insects, birds, and enthralled human visitors.

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    3. From Kathleen Soler via Facebook
      Dennis Dreher, I don't agree with you - I see herbicide being widely abused at the expense of the community that could be caring for these places, especially very young people. In the forest preserves I often see signs left up without dates, or worse yet, blue plants with no signs nearby. It's exhausting and sad to be constantly telling my child not to touch anything, or being hypervigilant instead of looking at the buterflies, insects, birds, and plants together. And yes, I am talking about myself, but no, I am not the only parent who can't stand that this is business -as-usual.

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    4. Kathleen Soler
      Dennis Dreher, I also appreciate the point that there might be some surgical interventions that are necessary - but not in, say, a managed, planted prairie at a public park, or a heavily used trailside.

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    5. While I agree with every word that Dennis Dreher wrote, I also have sympathy with Kathleen Soler. There's too much "one size fits all" mentality. A prairie planting in a public park should not have herbicide on the edges that could get on kids. A native species planting is utterly different from a rare, high-quality, seriously-threatened Nature Preserve. Toddlers do have to be supervised in any kind of nature because of poison ivy, briars, burs, yellow-jacket nests, weird people, etc. etc. For older kids, freedom to explore nature seems important. But even for them, Nature Preserves are rarely the best place for that, because there's no alternative to saying "no" more often than is good for children. I admire Kathleen's work to bring children to interact with nature in ways that work for both.

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  7. From Dan Carter via email:
    In the discussion of the forestry mow-foliar spray approach. There is still a common misconception that anything good that may be at a site, will be resurrected from the seed bank—that the seed bank is some kind of insurance policy. But that, of course, is wrong. Most of the conservative flora does not maintain a persistent seed bank, and many of the species hanging on at such sites have been vegetative for a long time, so their transient seed banks aren’t there either.

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  8. To understand some of the above-mentioned failures, people must first understand how herbicide is being applied. The below links are to video series forwarded to me by Christopher Evans from the Illinois Extension. These videos show typically suggested techniques.

    Cut Stump Applications
    https://www.youtube.com/playlist?list=PL9-thdquI6qO7Wf6zV5haw-4r4SJlLWP4

    Basal Bark Applications
    https://www.youtube.com/playlist?list=PL9-thdquI6qPsMJz7zWyWIoghqXcyti_a

    I specifically suggest viewing the video titled “Basal Bark Techniques.” This video shows various spray application methods and the “The Drizzle Approach.” Over spray is visible in the spray techniques. In the “drizzle” technique, herbicide runs down the stem to the ground. To minimize off-target damage, herbicide must not be sprayed on or runoff onto the ground. I describe the conditions (no rain for at least four days after, with more being better) and “no-drip technique” for basal bark applications that will allow off-target damage to be minimal in the comment section of the below blog post.

    https://woodsandprairie.blogspot.com/2023/08/bringing-your-game-to-herbiciding.html

    Despite how basal bark application is often misused causing a large “ring-of-death,” it is a valuable tool for ecological restoration when used as I described. As Dr. Stephen Enloe mentions in the video Cut Stump Application: Targets, “Additionally, for such a small stem you can really only get a limited amount of herbicide to move into that stem. And it is really not likely enough to kill large entire stumps or even lateral root systems coming off of those stems…” Therefore, when treating smaller woody stems with triclopyr ester in basal oil it is necessary to apply this herbicide to the basal bark to get good control. This is true regardless of whether the stem is cut or this herbicide is only applied to the basal bark. The below blog post has a graph that shows this fact with data collected at a local preserve the growing season after a winter workday.

    https://stewardshipchronicles.blog/2023/06/19/bluff-spring-fen-preliminary-results/

    If glyphosate is chosen to minimize risk of off-target damage in high-quality areas, there is a technique that will allow small woody stems to be killed during the dormant season using this herbicide. However, it is much more time consuming than basal bark application. I wrote up a treatise on this technique which is posted on the following blog.

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

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  9. From Don Osmond via email:
    As for which herbicide to use on crown vetch (CV), the best evidence favoring Milestone over Transline for CV is on the labels. The former is labeled to control CV, & the latter is not. If the manufacturer doesn’t list a species, either the herbicide is not effective on that species, was not tested on that species or results are too variable to be dependable. Bill Kleiman has published that Milestone worked on CV while Transline didn’t. Cook County Forest Preserves 2022 herbicide guide prefers Milestone over Transline.

    If someone focused on an old central patch where the root system is most robust, results will be worse than if they started at the edge (where the root system is weaker & more vulnerable) & worked inward. That also halts expansion, creating time for long term suppression of the central patch.

    Presence of thatch will hinder full coverage of stem & leaves, but since most sites aren’t burned annually, experiments are needed to see if mowing with a rotary or flail mower followed by herbiciding a few weeks later is effective. The positives are thatch reduction (if the plants are mowed into small pieces), removal of some native biomass to reduce off-target kill, resetting the plant into active growth mode & the fact that new shoots may not have yet developed traits to hinder herbicide absorption. The negative is if the plant is mowed into pieces that are too large, they may root themselves & make the problem worse. Also, the mower can spread those pieces far & wide.

    Mark Renz has published results that show October herbiciding was more effective than June (bud) or July (flower). A forest preserve ecologist said best translocation was April to mid June & mid August to early October. Wisconsin DNR recommends early spring when actively growing. Many sources, including the manufacturer of Milestone, recommend against spraying CV at bloom stage.

    Your warning on persistence is appropriate & it applies to both Milestone & Transline. If there were effective alternatives to these herbicides (that are also efficient for large sites with few resources), we would jump at the chance, but I’m not aware of any widely replicated alternatives. There is no easy answer & my current opinion is stopping an existential threat takes precedence over persistence or some off-target kill. Like the medical field, restoration is full of judgement calls for good reason & the best results for the most patients occur when we consider all the options & call a shot based on the best quality evidence while the patient is still alive.

    I agree consulting with an expert is needed before herbiciding in a remnant. Very tough call because not herbiciding may mean the loss of that remnant.

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    1. Don's good technical discussions are always appreciated. This post does not aim at presenting detailed best practices. It is basically conceptual and advocates for authoritative best management practices. As Don implies, it's a bit shocking how different the advice is from different sources. Once again, we are reminded of the need for a region-wide clearinghouse for best practices that updates advice as best evidence comes in.

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  10. For me the most important point of this blog is that evaluation of effectiveness of any restoration treatment (not just herbicides) must be the enhancement (or decline) of the native community within the treatment area. Native communities have many members with diverse interactions so it is not easy to do, but it is the goal. That must be the primary measure of effectiveness. Previous comments have not said much about that goal.

    Research is effective when there are one or two variables of interest (which explains the focus on the invasive target). The blog and comments list many herbicides, many application methods, precipitation after application, soil types, temperature, etc plus the care and knowledge of the actual applicator (the project planner is probably less important). In such situations science is not effective.

    How would I go about improving the situation? Have people submit information about their problem (area, species they want to reduce abundance of, species they want to increase abundance of). the work they did to solve it, and their results. All submiters and others experienced in natural communities evaluate the results. The quartile with the best results then become teachers of new people that want to learn to be stewards. The apprentice model will be much more effective than the research.

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    1. In the end, for a given location, the most important factors that determine how much herbicide needs to be applied for a given method are the size of the invasive species being treated and when the application occurs. It would not be difficult to train stewards what data needs to be collected from their efforts. This data could then be given to someone who has taken a college level statistics course and knows how to create a contour chart. The treatments are already being done. All stewards would need to do to increase effectiveness and reduce herbicide usage is to collect data, give it to someone who can make a chart, then use the chart when making future applications. Possibly, with data, it will be found there is not much variation between sites and the results would apply broadly.

      The amount of time until rain occurs after an application of triclopyr ester in basal oil is important in preventing the “ring-of-death,” but I have not observed it to alter the effectiveness of an herbicide application. The caveat is rain should not occur before a foliar application of herbicide dries. However, that is not very long.

      I know it is easy to throw up your hands and say, “Evaluating the ‘enhancement (or decline) of the native community’ is too difficult.” For me it has been as simple as applying herbicide and taking a picture. Returning to the location a few weeks later. Marking any plants showing damage. Taking another picture. Then returning the next year to see if the non-target plants that were impacted recovered.

      Interestingly, I have seen non-target plants do much better in subsequent years when I apply herbicide in the right way (lower part of stems or cut stems), at the right time of year (often fall), and being careful not to get it on non-target plants.

      As with any work, the more precise the task the more time (and therefore money) is required to complete it. Carefully applying herbicide takes much more time and effort than spraying. Resources are limited. I think the quality of work being done should be measured and reported. If people decide that they are happy with all the herbaceous plants and shorter woody species being killed by spraying, then so be it. I would hope people would choose a more costly method that would enhance the native plant community rather than destroy it.

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