Douglas Firs grow to 40-60 feet and spread 15-25 feet in an erect pyramid. They are the "perfect" Christmas Tree.
Due to EPA backlogs, ISCA MCH Douglas Fir Beetle Pouches may be delayed this year.
The pouches need a new EPA number for legal sale in the mountain West.
The EPA number has been requested. However, there is a backlog at the EPA (partly due to the government shutdown), and delivery is not guaranteed in time for the earliest part of beetle flight season.
Almost all pictures on this site were taken at or near our property near Estes Park, Colorado.
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The Douglas-fir beetle(Dendroctonus pseudotsuqae. Hopk.) infests and kills Spruce and Douglas Fir trees throughout most of its range in western United States and up through British Columbia. (not to be confused with the Fir Engraver Beetle, also a native bark beetle that attacks true firs. It does not attack Douglas-fir which is not a true fir.)
Colorado has been particularly hard hit. In Colorado, outbreaks typically occur in the southern part of the state, especially in portions of the Rampart Range, Wet Mountains, Sangre de Cristo/Culebra ranges, La Garita Range, West Elk and Elk mountains, and the southern slopes of the San Juan Mountains.
Normally, Douglas-fir beetles only breed in felled, injured or diseased trees, although epidemics occur where apparently healthy trees are colonized. In hot and dry summers, they can multiply quickly, breeding in slash, stumps, windfall and diseased trees as well as killing healthy firs and spruces.
Outbreaks typically start in blow-down, fire scorched areas, drought stricken, root diseased or areas defoliated by other insects. Use MCH in these areas to prevent a population build. If not prevented, the Douglas Fir Beetle population can "explode", attacking and subsequently killing healthy standing Firs.
Fir Beetles generally have a one year life cycle. But they start to fly EARLY in the spring. Snow may still be on the ground when the first flight occurs. They start in April and May, when temperatures consistently exceed 60 degrees F, and continue to fly and attack new trees until early June, depending on local conditions. Adults that emerge early may make a second attack later in the summer, typically from late June through August. Individuals that spent the winter as larvae typically emerge as adults in July or August.
MCH Application dates will vary a little with elevation but are typically started by Ap 15 (Get your snowshoes out!) and run through August with peak flights occurring from early June to early July.
In Spring, the newly hatched adults leave the tree of their metamorphosis, seeking out larger trees (usually over 8" diameter if possible) in the surrounding area. (In areas with heavy infestation, beetle hatchlings may take even smaller trees as pressure to get ANY tree increases). When the adults arrive, they begin tunnelling under the bark, lay eggs, which turn to larvae and live through the winter to produce more egg-laying adults to attack more trees. The larvae feed under the bark in the phloem layer, introducing fungi, yeasts, and other organisms that lead to tree death.
Trees attacked early in the Spring may actually produce new adults that will make a 2nd attack in late summer, but the "second flight" usually accounts for less than 10% of the infested trees.
It is estimated that one infested tree will kill at least two and possibly more trees. Thus the exponential devastation occurs.
There are few outward signs of infestation. Unlike mountain pine beetles, there are no pitch tubes. Look for small mounds of 'sawdust' (boring dust called Frass) at the base of the tree and in the bark crevice. Boring dust is left when the beetles bore into the bark of the tree. This will have the consistency of flour or fine sawdust and will be reddish in color. However, frass can wash away and attacks may be above eye-level, making it difficult to locate attacked trees. While pitch-tubes are not usually present, many trees will have pitch streaming (clear resin) down the tree bole from the top of the beetle-colonized area.
"Rusting" tree tops are often the first sign of tree damage. Trees will begin to have dead tops and boughs in the summer after infestation and will usually die by the following Spring. Tree foliage discolors several months to a year after the attack, transitioning from green to reddish brown in that time.
It is critical to remove and properly dispose of infested trees and slash prior to trying to deter beetle populations from attacking good trees in the stand.
Quick Guide to Signs of Fir Beetle Attack
This is the most important bark beetle on Douglas-fir throughout its range, and it is not easily confused with other beetle attacks on Douglas Fir trees.
As always, the best defence against Douglas Fir Beetle is a healthy stand of trees that are able to defend against attack. Proper spacing, basal area, water and removal of brood trees and unhealthy trees are all important.
MCH is widely used by the USFS for preventing attacks on valuable Douglas Fir stands. Dense stands of large Douglas Fir trees are at highest risk of attack. If direct control is deemed necessary, trees can be protected using the anti-aggregation pheromone methylcyclohexanone (MCH), which disrupts beetle aggregation. Combining MCH with salvage of infested trees has been successful at reducing subsequent tree mortality.
Spruce beetle populations range from Alaska and Newfoundland to as far south as Arizona and New Mexico. The subalpine Engelmann spruce is the primary host tree, but the beetles will infest any spruce tree species within their geographical range, including blue spruce. In Colorado, the beetles are most commonly observed in high-elevation spruce forests above 9,000 feet.
While Blue Spruce are only occasionally attacked, Engelmann spruce trees over 16 inches in diameter are most susceptible to spruce beetle; trees less than 5 inches in diameter are seldom attacked. Freshly killed or damaged trees (e.g. from windthrow or avalanches) are preferred habitat.
The patterns of spruce bark beetle infestation over the landscape correlate most strongly with patterns of windfall episodes, and less so with patterns of temperature and precipitation, which makes sense as they prefer downed trees. Higher temperatures will favor the beetles and induce a transition from one to two generations per year in some areas.
Spruce bark beetles are capable of killing trees only when they reach a certain number. Long-term drought and other factors that weaken the trees' resistance are important, because they determine how many beetles are needed to conquer living trees. The number of weakened trees builds up during the interval between outbreaks, and such trees are quickly consumed during an outbreak. Weakened trees thus function as a kind of fuel for the outbreaks.
Spruce beetles may complete their life cycle in 1 year on warm sites at lower elevations or take up to 3 years in cool, well-shaded locations on north slopes. However, throughout most of its range and in most seasons, two years are generally required for the spruce beetle to complete its life cycle.
Like the Mountain Pine Beetle and the Fir Beetle, females bore into the tree, lay their eggs, and let nature take its course. After the eggs hatch, the spruce beetle larvae spend the winter developing under the bark of their host trees. During the second winter of the 2-year life cycle in standing trees, some beetles overwinter in their pupal sites but the majority, often as high as 95 percent, of the new adults emerge, move to the base of the tree, and bore into the bark near the litter line to overwinter. Overwintering at the base of the infested tree reduces predation by woodpeckers and reduces winter mortality due to extreme cold temperatures. There they lye in wait for Spring to emerge as adults.
Although adults may emerge any time from May to October, depending on temperature, most attacks occur in early summer. Dense stands of large Spruce trees are at highest risk of attack. Look for signs from Mid-May thru July and use MCH to repel the beetles starting in early May in most elevations.
Scientists have found that drought negatively affects Engelmann spruce trees, which then have weaker defences against Spruce beetle (Dendroctonus rufipennis), triggering an outbreak in hundreds of thousands of acres in Colorado's forests.
As of 2012, fewer acres of Colorado trees have been affected by spruce beetles than mountain pine beetles, but there are more spruce forests in Colorado than Lodgepole pine, so there's "no reason to expect the percentage mortality to be less or acreage affected to be any less" than it was for the mountain pine beetle epidemic, said Tom Veblen, coauthor of one of the studies and a geography professor at CU.
More than 311,000 acres were killed by spruce beetles in Colorado in 2012, compared to 64,000 acres in 2008, and infestations are going strong, especially in southern parts of the state like the San Juan and Rio Grande National Forests.
Of course that was 5 year ago. An article published by the Denver Post in October 2017 headline reads "Southwest Colorado forests under attack by pine beetle". Gretchen Fitzgerald, a forester for the U.S. Forest Service’s Columbine District, which manages nearly 700,000 acres of the San Juan National Forest in La Plata and San Juan counties says, "Over the past two decades, more than 120,000 acres of the Weminuche Wilderness — Colorado’s largest designated wilderness area at 488,210 acres — have fallen prey to the destructive spruce beetle."
Spruce beetle continues to spread southward from Colorado, where it has caused extensive spruce mortality - a 55% increase from last year - in New Mexico. Given the heavy spruce beetle activity in southern Colorado, the threat for further massive spruce mortality in New Mexico is high - particularly in the northern half of the state.
As always, the best defence against Spruce Beetle is a healthy stand of trees that are able to defend against attack. Proper spacing, basal area, water and removal of brood trees and unhealthy trees are all important.
Beetles and other insects communicate using pheromones. MCH - a synthetic pheromone treatment for Douglas Fir & Spruce trees - replicates the beetle pheromone, sending a message that the tree is full to capacity and that the food supply is insufficient for additional beetles. Arriving beetles receive the `message' that they should look elsewhere for a suitable host tree.
MCH is non toxic pheromone control for use against Douglas Fir Beetles (Dendroctonus pseudotsugae (Hopkins) and Spruce beetle (Dendroctonus rufipennis). It is contained in a small bubble-cap that emits a simulated pheromone (naturally produced by the beetles) and tells incoming beetles that a tree is full when in fact it is not. Fooled by the phantom communication, they continue to fly to find another host tree. With little capacity for long flights, a significant number will die in transit looking for another place to raise their brood.
MCH is environmentally safe and non-toxic to humans, pets, birds, and even the beetles themselves. Registered by EPA and most Rocky Mountain States. All pheromones in controlled release dispensers are approved organic by USDA/NOP. It is user and Eco-Friendly. Unlike the insecticides approved for Bark Beetle control, MCH does not kill bees, beneficial insects, aquatic organisms. Not restricted use. Always follow label instructions.
MCH comes in easy-to-use controlled-release bubble dispensers that are hung on un-infested trees or placed in a grid pattern when wanting to protect acreage. MCH packets should be applied to trees before adult beetles begin to emerge, which in Colorado (a very hard-hit area) is typically April or May. They also need to be applied to dead logs or blowdown where possible. (see "Stumps" below) Bubbles have been designed specifically to last as long as the beetle flight and do not need to be replaced half way through the season in most instances.
For individual trees: It is our recommendation that you staple or nail the first 1-2 MCH caps 7 - 10 feet high (2m) on the north face of the tree just prior to beetle flight season. MCH Application dates will vary a little with elevation but are typically Apr 15 - May 1 for fir beetles and June 1 thru June 15 for Spruce beetles. For larger trees add 1 bubble cap for each 8" in diameter 3 ft above the first cap. (a tree 16" in diameter will have at least 2 bubble caps with 1 or 2 placed at 6-12 feet height and on additional 1 at 12 - 14 ft height.
Tree areas less than 2.5 acres: Place 1 or 2 bubble caps on all trees over 8 inches in diameter, the number of bubble caps depending on risk of attack. OR employ a grid pattern throughout. Area-wide protection is the most economical method. Areas 1/2 acre or larger can be protected by placing Bubble Caps in a grid fashion, spacing the product every 30-35 feet. (The effective radius of the pheromone plume is about 15 feet, so try to space the caps no more than 30 feet apart). Remember, you do not need to place MCH directly on the tree. If you do not have a pine or fir tree conveniently spaced every 25 feet, you can apply MCH to any other tree, a post hammered into the ground or even a building. You are trying to create an invisible blanket of MCH pheromone that surrounds and permeates the wooded area. Use approximately 30-40 BeetleBlock bubble caps per acre applied in this fashion.
Stumps and wind-thrown trees: Each stump or tree must be treated to prevent population build-up because stumps and wind-thrown trees are preferred hosts. Place 1 bubble cap on the north face of each stump. Place up to 6 bubble caps, depending on the tree size, at 6 - 10 foot spacing on the shady side of the log.
Winds: The wind speed and direction determines where the pheromone plume will go. It is also important to note that pheromone products are volatile chemicals and insects can only `sense' these chemicals from a down wind position. If possible, use the wind factor to your advantage. Additionally, the pheromones disperse from the capsules more quickly as the temperature warms up. By using the north face of a tree, you are usually placing them on the cooler side AND on the upwind side.
Studies have shown that during epidemic conditions, the pressure from beetle populations who must go SOMEWHERE (even if conditions are not optimum for them) may reduce the effectiveness of all treatments. Given the "find a tree of any size or perish" imperative that emerging pine beetles face, they may habituate to both chemicals and pheromones. However, we still have a few years to work on the problem in areas that are not yet overrun. That time may give just the breather necessary to let nature begin to draw back the danger or for other management techniques to take hold.