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Ice, snow and deep frost: winter creates problems for trees

By forest health specialists Linda Williams, Woodruff, Linda.Williams@wisconsin.gov, 920-360-0665; Mike Hillstrom, Fitchburg, Michael.Hillstrom@wisconsin.gov, 608-513-7690; Alex Feltmeyer, Plover, Alexandra.Feltmeyer@wisconsin.gov, 715-340-3810

Heavy ice and snow loads can cause significant problems for trees. Branch tips and whole branches may break under heavy loads, and in windy conditions entire tree tops can come crashing down.

Freezing rain on February 4, 2019 covered trees around the state with a ¼” thick layer of ice. The weather then turned bitterly cold, leaving the ice stuck to the branches, weighing them down and straining the trees. Following that event, a snow storm affecting most of the state led to more ice, snow and damage to branches. 

Tree branches covered in 1 inch of ice.

These extraordinary ice formations may look light and frosty, but they add a lot of weight to tree branches and can cause branch breakage.

Some trees are more susceptible to winter damage. Small trees can be particularly prone to injuries caused by heavy ice and snow. They can bend so far over from the weight that their tops are near or even touching the ground. In some cases, their stems may break at ground level causing the entire tree to fall over. Other vulnerable trees include those with ingrown bark at branch unions. This type of branch union is weak and more likely to split under heavy loads.

White pine saplings bent over from weight of ice on branches.

These young white pines were coated in ice, causing them to bend over. They may not rebound well after the ice and snow melt.

White pine sapling weighed down with snow, causing significant branch droop.

The heavy snow on the branches of this young white pine have caused the branches to droop and the top to bend over significantly. Heavy snow loads can cause branches to break.

While forest trees are just as prone to winter damage, yard trees present the most safety hazards and should be seen by an arborist as soon as damage becomes evident. Storm-damaged trees may have dangerous features such as hanging branches, branches under tension, spring poles and cracks in the main stem. Depending on the damage, some yard trees may also require pruning to correct their form and protect them from future injuries. Due to the dangers associated with storm-damaged trees, consider having a professional arborist or logger do your tree pruning or removal.

Tree roots can be damaged in cold weather too. In areas of southern Wisconsin, a lack of snow during some of this winter’s cold snaps has forced the frost deep into the ground. Some of you may recall the winter of 2002-2003 when we had very little snow and frost went 5’ deep in many parts of the state. Not only did it freeze septic systems and water lines that winter, but it also damaged tree root systems by killing some of the fine roots and root tips that grow deep below the surface and prefer not to freeze. Trees that lost a significant number of roots experienced crown dieback and stress that led to insects and diseases attacks, including two-lined chestnut borer on oak and Armillaria root rot on conifers. Deep freeze damage to tree roots is not often the single cause of tree stress or death but is more often one of several stress agents that leave trees more susceptible to insects and diseases. Fortunately, the deep frost can be pulled out of the ground, and some of the damages avoided, if there is enough snow cover for the remainder of the winter.

For more information on how snow and ice can impact trees, check out these resources from Wisconsin [PDF] and Minnesota. Contact a certified arborist or DNR forester if you want to discuss management options for storm-damaged trees.

Revised emerald ash borer guidelines now available

By Bill McNee, forest health specialist, Oshkosh, Bill.McNee@wisconsin.gov, 920-360-0942.

The Wisconsin Department of Natural Resources has released updated guidelines to aid woodland owners and managers in managing ash stands in light of the invasive emerald ash borer (EAB). The guidelines that became effective on January 1, 2019 reflect new research, increased pest detections and the anticipated transition to a statewide EAB quarantine (which occurred in March 2018).

Forestry professional and landowner standing in hardwood stand assessing conditions.

Landowners should work with professional foresters to make management decisions related to EAB on their land.

The silvicultural guidelines are intended to help make informed stand-level decisions regarding management of stands that are not yet infested by EAB and stands that are already impacted by the tree-killing beetle. They should be used along with other materials, including best management practices and other guidance documents, to develop appropriate management plans. 

The revised guidelines include recommendations to:

  • Implement management plans as soon as practical, across all of Wisconsin, to reduce a stand’s ash component to no more than 20%. More management options are likely to be available by taking immediate action
  • Review existing management plans to determine if they need revision due to changes in EAB distribution, stand condition, market prices, etc.
  • Diversify woodlands with site-appropriate tree species
  • Utilize merchantable ash before trees are infested or killed. It may be appropriate to retain some live ash on site for ecological benefits, species diversity, wildlife habitat, temporary cover or seed production

The guidelines also place a greater emphasis on assessing stand and site conditions before making management decisions. The document offers stand management alternatives for both upland and lowland stands, while recognizing that conversion of lowland ash stands to other forest types will be impractical in many cases.

If you would like more information about emerald ash borer or these guidelines, visit the DNR EAB webpage or talk to your regional forest health specialist.

Revised Heterobasidion root disease guidelines now available

The Wisconsin Department of Natural Resources has released updated guidelines to reduce the risk of introduction and spread of Heterobasidion root disease (HRD) in Wisconsin through preventive stump treatments. The revised guidelines became effective on January 1, 2019, and a professionally designed version will be available soon. Woodland owners are strongly encouraged to work with a professional forester to make management decisions about HRD and preventive stump treatments.

Pocket of HRD-caused thinning and mortality in red pine plantation, Grant County.

Pocket of HRD-caused thinning and mortality in red pine plantation, Grant County.

Heterobasidion root disease is one of the most destructive diseases affecting conifers in the Northern Hemisphere. In Wisconsin, HRD is most commonly found in pine and spruce plantations. Infection by the wood-decaying Heterobasidion irregulare fungus kills living tissues and leads to growth loss and tree mortality. Spores landing on a fresh cut pine or spruce stump will infect that stump and root system and spread via root contact to neighboring trees, killing them as it invades their root systems. This pattern of spread creates pockets of dead and dying trees that expand outward. Growth reduction of trees leads to economic losses for plantation owners, and mortality of trees, including seedlings and saplings, has long-term implications for future stand composition and management.

The HRD stump treatment guidelines are designed to help make decisions about the use of preventive stump treatments when harvesting a stand. These treatments limit disease introduction by preventing fungal spores from developing on the exposed surfaces of newly cut stumps.

Cutting bar on logging equipment spraying blue chemical used in HRD stump treatments.

Pesticides used in stump treatments can be applied using logging equipment (blue mist exiting through nozzles in saw bar) or backpack sprayer.

Stump treatments are typically recommended between April 1 and November 30 if a stand is within 25 miles of a known HRD infection site and the stand is more than 50% pine and/or spruce. However, there are other factors to consider when deciding whether to use the preventive stump treatments. Certain situations when you may not need to treat stumps, referred to as “Exceptions” and “Modifications” in the guidelines, consider variables such as economic feasibility, landowner risk tolerance, unexpected weather patterns and future desired stand composition. Highlights of the revised stump treatment guidelines include:

  • Timing of treatments and general distance recommendations did not change from older guidance
  • Addition of spruce as a species recommended for stump treatment
  • Additional Exceptions and Modifications where treatment may not be necessary
  • For private landowners with a higher risk tolerance, a 6-mile radius from known infection sites can be considered when evaluating whether to apply treatments
  • Even if a stand is considered at low risk for HRD infection, woodland owners should carefully consider the potential impacts to their stand if preventive treatments are not used and HRD becomes established

Along with the guidelines, a web-based HRD map viewer has been launched. This interactive map displays confirmed HRD locations and 25-mile and 6-mile radius buffers around HRD locations. The purpose of this map is to help users determine whether a stand is within either the 25 or 6-mile buffers where stump treatments are recommended. You can enter an address or GPS location, turn map layers on and off, and zoom in and out to an area of interest.

If you would like more information about HRD or these guidelines, visit the DNR HRD webpage or talk to your regional forest health specialist.

2018 Forest Health Annual Report now available

The Forest Health Annual Report summarizes notable impacts pests, diseases and weather on the health of Wisconsin’s forests. The report is a collaborative product written by DNR forest health specialists from around the state. It outlines the damage and spread of both native and invasive pests and diseases during that year and puts these into context of observations from previous years. Management programs and their results are also described. Highlights from the 2018 annual report include:

  • American beech with resistance to disease-causing scale insect entered into a breeding program for species conservation and reintroduction
  • Confirmation of jumping worms in northern counties
  • Biological control of emerald ash borer
  • Closure of the state gypsy moth suppression program
  • Innovation in survey of the invasive plant lesser celandine
  • Dieback and mortality in balsam fir caused by freezing weather in April followed by unseasonably hot temperatures in early May

The 2018 report and others dating back to 2003 are available on the forest health publications page. Historical reports dating back to 1951 are archived and available upon request. Contact Marguerite Rapp at marguerite.rapp@wisconsin.gov for more information on the archived reports.

Jack pine budworm not likely an issue in 2019

By Todd Lanigan, forest health specialist, Eau Claire, Todd.Lanigan@wisconsin.gov, 715-210-0150. 

No caterpillars or egg masses were found in the 2018 jack pine budworm surveys. Done in the spring for caterpillars and the fall for egg masses, surveys help predict jack pine budworm defoliation in the coming year. Surveys were conducted in the west central part of the state, covering portions of Dunn, Eau Claire, Jackson, Monroe, Pierce and St. Croix counties. 

Jack pine budworm caterpillar on spruce needle tip.

Caterpillars emerge in the spring and feed on host tree foliage. 

Cluster of jack pine budworm eggs on tip of spruce needle.

Egg masses are deposited on the tips of host tree foliage. 

In Wisconsin, jack pine budworm feeds on all native species of pine: jack, red and white. It is occasionally found on white spruce, but this has only been documented where spruce trees were located near an infested pine plantation.

Jack pine budworm regularly cycles from low to high populations, with outbreaks occurring every 8-10 years on average. During an outbreak, defoliation from these caterpillars can be widespread and lead to growth loss, topkill and tree mortality.

Three host trees showing severe defoliation and mortality due to jack pine budworm defoliation.

During a jack pine budworm outbreak, defoliation and mortality can be severe.

Wisconsin forests are overdue for an outbreak, with the last one occurring from 2005-2009, but annual surveys indicate that populations of jack pine budworm are still low enough to be undetected. Based on the 2018 surveys, jack pine budworm should not be a problem in 2019.

Trapping project found no non-native beetles

By Mike Hillstrom, forest health specialist, Fitchburg. Michael.Hillstrom@wisconsin.gov; 608-513-7690

The Wisconsin DNR’s forest health team received funding to trap for non-native beetles in 2018. This project was funded by the US Forest Service through an Early Detection and Rapid Response (EDRR) grant. The project is complete, and we happily share that we did not find any non-native beetles!

Forest health staff member Scott Schumacher is hanging a Lindgren funnel trap (12 funnels stacked to look like a tree trunk) from a tree branch to survey for non-native beetles.

Forest health staff member Scott Schumacher hangs a Lindgren funnel trap to survey for non-native beetles.

The Forest Service periodically provides funding to states to trap for non-native bark and ambrosia beetles. The goal of trapping is to detect, delimit and monitor newly introduced exotic beetles and to quickly assess and respond to newly detected infestations.

We placed traps at 12 high-risk sites in Jefferson, Waukesha, Milwaukee, Racine, Manitowoc, and Brown counties. Sites were selected in collaboration with the Wisconsin Department of Agriculture, Trade and Consumer Protection and were based on proximity to large commercial port entries on Lake Michigan or recycling facilities for pallets and other waste packaging. Three Lindgren funnel traps (12 funnels stacked to look like a tree trunk) and lures were assembled at each site and checked every two weeks between early May and early August. Specimens collected from the traps were sent to a Forest Service taxonomist for identification.

New northern oak wilt detections

By Paul Cigan, forest health specialist, Hayward. Paul.Cigan@wisconsin.gov; 715-416-4920 and Linda Williams forest health specialist, Woodruff. Linda.Williams@wisconsin.gov; 920-360-0665

Oak wilt (OW) was confirmed for the first time in Bayfield and Douglas counties and in 16 new northern townships in 2018. The new OW infections occurred on a range of properties, including county, tribal, private, U.S. Forest Service and Board of Commissioners of Public Lands. Wisconsin Department of Natural Resources (DNR) forest health staff are working proactively with affected property managers and landowners to address these infections and prioritize disease prevention and detection in the future.

 

Oak wilt distribution map. Confirmed counties are displayed in red. Confirmed townships are displayed in pink 6-mile square blocks.

The greatest risk of overland transmission in northern Wisconsin is from April 15 to July 15, when fungal spores readily infect open wounds. Most of these new cases occurred during this time frame due to stem and branch damage. The primary causes of damage were roadside brush clearing, pruning, lot clearing and storm-caused branch breakage. Fungal spores may have come from diseased oak firewood and unprocessed wood recently transported into these areas.

Image shows a group of oak trees. Northern red oak on far left is in wilting stage of disease (leaves on but wilting and dropping). Oak on far right has mechanical root collar injury. Dairyland Township, Douglas County.

OW disease center. Oak on far left was infected through belowground root contact with tree damaged in lot clearing (far right). Dairyland Township, Douglas County (photo taken by Paul Cigan).

If oak wilt is present in or within 6 miles of the county where you manage oak, your management activities may be affected by seasonal harvesting restrictions to reduce OW introduction and impact. Read DNR’s oak harvesting guidelines for more information and refer to the list below of new 6 square mile blocks by township and county to see if OW has been detected near your property.

Bayfield County
Barnes T45N R9W
Cable T43N R7W
Drummond T45N R8W
Douglas County
Dairyland T43N R15W
Gordon T44N R11W
Langlade County
Elcho T34N R11E
Langlade T33N R13E
Neva T32N R11E
Sawyer County
Couderay T39N R8W
Hayward T41N R8W
Hunter T40N R7W
Round Lake T41N R8W
Spider Lake T42N R7W
Vilas County
Boulder Junction T42N R6E
Lac du Flambeau T41N R5E, T40N R5E
St. Germain T40N R8E

Please report any suspected oak wilt infections to your local DNR forester or regional forest health specialist and learn more about oak wilt identification and biology on the DNR oak wilt webpage. To learn more about firewood rules and how you can help reduce transmission of pests and diseases, including oak wilt, visit the DNR firewood page.

10 oak leaves lain on downed log display bronze discoloration typical of oak wilt. Midrib and base of leaf are still green.

Bronzed leaves fallen from infected oak. Leaves were observed beneath infected northern red oak. Cable Township, Bayfield County (photo taken by Paul Cigan).

Heterobasidion root disease in Monroe County

By Todd Lanigan, forest health specialist, Eau Claire. Todd.Lanigan@wisconsin.gov; 715-210-0150

Heterobasidion root disease (HRD), formerly known as annosum root rot, was recently found in Monroe County for the first time in the town of Little Falls. With this detection, HRD is now known to occur in 28 Wisconsin counties.

HRD distribution map. Counties where HRD is present are shown in blue with most recently confirmed county shown in dark blue.

Fruiting bodies of the pathogen, Heterobasidion irregulare, were found on dead overstory red pine and both live and dead white pine saplings in the Big Creek Fishery Area. The 20-acre stand was a red pine plantation established in 1958 and last thinned in 2012. Wood samples were collected to isolate and identify the pathogen through microscopic identification at the Forest Health Lab in Fitchburg.

Image of multiple spores viewed under microscope. Conidiophores look like Q-tip heads.

Microscopic spores isolated from wood samples and confirmed as HRD in Forest Health Lab.

Based on this new find, a number of townships were added to the 25-mile buffer zones used in determining appropriate management activities according to the HRD Management Guide. There will be a one-year grace period for implementation of the guide in these townships.

The Forest Health Program has records of all confirmed HRD detections. If you suspect this disease is present in a stand, contact your regional forest health specialist.

For more information about HRD, visit the DNR Forest Health webpage.