Bark Beetles 1
Lecture Outlines/goals
- Introduction
- Diversity
- Roles and impacts
- General Biology
- Brood (offspring) production
- Emergence/dispersal
- Colonization
Bark Beetles
(Coleoptera: Curculionidae: Scolytinae) Feed within subcortical tissues (e.g. phloem) of virtually all parts of woody and herbaceous plants
- Roots
- Stems/boles
- Branches/twigs
- Fruits/cones
Generally mono- to oligophagous
- They only like one (mono) to a few species (oligophagous)
Most commonly associated with conifers as disturbance agents
- High diversity in conifer ecosystems
Roles and impacts
Consumption of phloem tissue kills part or all of a tree
Ecological roles:
- Succession
- Species removal
- Soil nutrient cycles
- Decay processes (e.g. fungi)
- Fire cycles
- Ecosystem renewal
Socio-economic impacts:
- Production forestry
- Decaying dead trees non-merchantable
- Aesthetics
- Loss of high-value trees on private lands
- Wildland-urban interface
- Fuel loading, fire risk
- Tree failure
- Biodiversity/endangered species
- Ecosystem alterations
- Water quantity/quality
- Watershed alteration
- Carbon dynamics
- CO2 release from dead organic matter
General Biology
Brood production
- Mating
- Gallery construction
- Oviposition
- Brood Development
Males or females initiate attacks (species dependent) Male initiators = males excavate nuptial gallery for mating
- Multiple females (polygamous)
- Egg galleries (one per female) extend from nuptial chambers
Female initiators = mating at bark surface
- Most species +/- monogamous
- Females create single egg gallery
Gallery patterns (with host-tree identification) often characteristic of species
Gallery creation versus tunneling/scoring
- Galleries are created by multiple, related individuals (offspring/sibling) whereas tunnels are created by one individual
Females:
- Lay eggs singly or in groups in niches along margins of gallery
- Niches packed with frass
- Fecundity from several to 300 eggs/females
Males
- Frequently assist females by cleaning galleries
- Adaptations for clearing frass/boring dust:
- Elytral declivity, flattened head capsule, hairiness
Brood production 3
- Larvae feed and develop through several instars Silviculture/Biotic Disturbances/Module-1/Definitions
- Pupation occurs in enlarged chambers at the end of larval galleries or in common feeding area
- Young (i.e. tuneral) adults often feed to complete maturation (increase flight muscles, acquire symbionts, sclerotize (harden))
- Mature adults cut exit hole to outside
- Maturation feeding may involve other plant parts (e.g. European elm bark beetle)
Brood production 4
- The number of generations per year (i.e. voltinism) may be less than 1 (semivoltine) to 7-8 (multivoltine)
- One generation per year (univoltine) most common in Canada
Brood Production 5
Temperature is very important (based on elevation or latitude or both)
- Within a species, the number of generations per year may vary with climatic conditions
- Climate-related population asynchrony may cause significant mortality
- Delayed/advanced development cause cold susceptible stages to overwinter
- Prolonged adult emergence reduces chances of mating
Emergence/dispersal
-
Flight
-
Host selection
-
Environmental impacts
- Temp, humidity, light
-
Optimal temperature and humidity required for emergence and flight
-
Avoid rain and winds > maximum flight speed
-
Short window of emergence to maximize chances of finding mates/hosts
-
Flight period may be required before beetles become receptive to cues from hosts or conspecifics (other beetles)
- Ensures population dispersal, minimizes intraspecific competition.
-
Dispersal both short and long range
-
Most beetles fly beneath canopy (short-range dispersal, upwind flight when seeking hosts or mates)
-
Small percentage fly above canopy (long-range dispersal)
Host selection (primary attraction)
- Cues
- Light/temperature (stand density)
- Visual (large vertical silhouettes)
- Olfactory (e.g. ethanol, terpenes)
- Cascade of decisions:
- Host versus non-host species
- Susceptible versus resistant
- High versus low quality
- Presence/absence of competitor species
- Presence/absence of conspecifics
Colonization
-
Beetle-tree interactions
-
Mortality factors
- Tree defense
- Competition
- Predation
-
Host acceptance based on gustatory stimulation (i.e. taste)
-
Following acceptance (by pioneer beetles)
- Release of aggregation pheromones (both sexes)
- Response by conspecifics (secondary attraction)
Trees produce resin as defense against attacks
- Most bark beetles select trees with impaired defenses
- Drought, disease, windthrow, suppression, age
- "secondary species"
- Some species don't care
- "primary species"
Primary beetles:
- Preferentially attack large diameter vigorous trees
- Succesful attack requires tree mortality
- Occasionally undergo population eruoptions (i.e. outbreaks) and cause mortality over landscapes
Secondary:
- Preferentially attack suppressed trees
Tree defenses
- succesful colonization contingent on tree death
- Trees have evolved defensive responses
- Constitutive resinosus
- Preformed resin ducts or pockets exude pitch
- Mainly physical barrier
- Induced resinosus
- Cellular necrosis (autolysis) and release of toxins
- Defense = vigour
Symbionts
Evolved to carry one or more species of fungi
Symbiosis: two unlike organisms living together for mutual benefit All bark beetles carry symbiotic organisms - mostly fungi Mutual benefits
fungi | beetle |
---|---|
Transport to new host | tree pathogen |
blank | habitat modification |
blank | nutrition |
Mycangia (adj. = mycangial)
- structures that carry and sometimes nurture fungal spores
- Located mainly on head or mouthparts
Phoresy (ad. = phoretic)
- Spores carried on body
Semiochemicals:
- Chemical messengers
- Insect-modified tree defenses
- Pheremones: Cause a specific reaction in a receiving organism of the same species
- E.g. aggregation, anti-aggregation
- Kairomones: Evoke in the receiver a reaction that favours the receiver but not the emitter
- E.g. host/prey location
- Allomones: Evoke in the receiver a reaction that favours the emitter, but not the receiver
- E.g. interspecific territoriality
- Potential multifunctionality
- E.g., one species' pheremone = another species' kairomone
Competition
- Intraspecific competition significant density-dependent mortality
- Optimal attack density to overcome tree resistance before competitive effects
- MEchanisms to minimize overcrowding: stridulation (chirping)
Resource quality:
- Tree quality = phloem thickness
- Better nutrition
- Less competition
- Faster development
- More offspring
Abiotic mortality factors
- Largest source of mortality following colonization
- Primarily temperature related
- Direct effects on beetles
- Growth and development
- Survival
- Indirect effects on host trees
- Phloem moisture
- Beetle adaptations:
- Diapause
- Cold tolerance
- Cold-related mortality greatest during unseasonable events
- E.g. cold snaps in autumn or spring
- Direct effects on beetles
Bark Beetle Management
Sampling bark beetles
- Pheremone-baited multple funnel traps (i.e. Lindgren traps)
- Best for presence/absence detection (i.e. monitoring)
- Pheremones only 1 cue considered by foraging beetles
- Best for presence/absence detection (i.e. monitoring)
- Aerial and ground surveys
- Aerial (low altitude fixed- or rotary-wing aircraft) detection of last years red attacked trees followed by ground surveys to detect new green attacks
- Trees attacked in one year do not reliably show symptoms in crowns until the following year once beetles have finished development
- Red attack tree = where beetles were not are
- Green attack trees = signs of beetle colonization on bole only
- Aerial (low altitude fixed- or rotary-wing aircraft) detection of last years red attacked trees followed by ground surveys to detect new green attacks
- Aerial overview surveys
- Since 1959, BC has employed annual aerial surveys. Some of the best data in the world.
- Broad (high altitude fixed-wing aircraft); surveys of landscapes to assess population distribution and tree mortality
- Suitable for extensive epidemics
- Remote sensing
- Much promise, slow adoption
Two approaches
-
(indirect) Modify existing stands to make them less good for beetles
-
(direct) Or look for problematic populations and manipulate those populations
-
Indirect control (proactive) = management of populations through tactics that reduce forest susceptibility (not yet widely operational, but is what we should be doing)
- Long term
- Species and/or age mosaics
- Harvesting/prescribed fires
- Stand modification (silviculture)
- Host removal from mixed stands
- Vigour maintenance for "pre-susceptible" stands (e.g., pre-commercial thinning)
- Spacing to increase vigour of susceptible stands
- Indirect control is irrelevant during outbreaks because too many beetles
-
Direct control (reactive) = management of populations through tactics that kill populations early
- Short term
- Reduction of beetle pop'n
- Strategy = population reduction greater than yearly population increase
- Tactics:
- Chemical tactics irrelevant and unacceptable
- Bark beetles live under the bark of trees and are not exposed to any chemicals we could apply
- Not legal in Canada
- Environmental concerns
- Cultural/mechanical tactics
- Fire
- Single trees felled, bucked, and burned on stump
- Broadcast burning - unsuitable for direct control
- Crown fires required for significant beetle mortality
- Debarking
- Harvesting and processing
- Single trees
- Stands - sanitation logging
- Trap trees (note: spruce beetle, Douglas-fir beetle only)
- Leave highly susceptible trees/logs behind for beetles to infest, followed by prompt removal and destruction
- Semiochemical tactics (in combination with above)
- "post-logging mop up" -- aggregation pheremones in residual trees after logging
- "Containment and concentration" - aggregation pheremones in harvest blocks before logging
- "Push-pull" - anti-aggregation pheremones in unharvested areas, aggregation pheremones in harvest blocks
- Fire
- Chemical tactics irrelevant and unacceptable
Management Theory
Direct control: a framework for success
- Rate of Increase (R) = 2 == roughly 500 trees killed by year 10
- 190 rees saved by removal of 3 of 8 infested trees in year 4
- Population continues to increase though
- 190 rees saved by removal of 3 of 8 infested trees in year 4
- Control must exceed rate of increase
- P greater than 1-1/R (R = rate of increase) (P = proportion of trees treated)
- How much is enough?
- Use credit card payment formulas
Examples of success
Banf, Alberta - 1940's
- Incipient MPB epidemic
- Entomologist + very large crews
- All trees surveyed over 2 years, infested trees destroyed
- Epidemic suppressed by year 3
Take home messages
- Successful direct control strategies require detailed knowledge of:
- Population size (and location)
- Potential rate of increase
- Look under bark and record how many eggs laid by females
- Alternatively, look at spread
- Direct control tactics must:
- Be early and aggressive
- Treat more than the anticipated growth in the pop'n given its size and rate of increase
- Persist as long as causes of pop'n increase remain operative (or until management objectives are achieved)