Title: Biological Control of Weeds
1Biological Control of Weeds
- Peter B. McEvoy
- Ent 420/520
- Oregon State University
2Biological Pest Control
- Scope of weed biocontrol
- Historical highlights
- Stages in Project Development
- Determining host specificity
- Selecting target and control organisms
- Ecology as an explanation and guide for biocontrol
3Scope of Weed Biocontrol Excludes
- Weed species of value
- Weeds closely related to crop plants, widely
planted ornamentals, or valued native plant
species - Weeds that require immediate control
- Weeds that need to be eliminated from an area or
can be tolerated only at very low densities - Weeds that are geographically localized or have
minor importance - Weeds of cropland under intensive cultivation,
frequent crop rotation, or heavy pesticide
treatment
4Historical Highlights
- 1795 - First transfer between countries
- 1903 - Pioneering foreign exploration
(Lantana) - 1925 - Outstanding early success (Opuntia)
- 1951 - First control of native weed (Opuntia)
- 1945-46 -A successful transfer project
(Hypericum) - 1964 - First aquatic weed (Alternanthera)
- 1961- First annual weed (Tribulus)
- 1960-70s - First control of cropland weed
(Chondrilla)
5Stages in Project Development
- Domestic Surveys
- Literature searches to learn about target-weed
- Pre-introduction surveys of fauna
- Scoring system for selecting target weed
- Foreign exploration and selecting promising
candidates for screening - Host specificity determination
- Importation, Release, and Establishment
- Evaluation of results
6Classical Biological Control of Weeds Not a
panacea, Not risk free
Alien Plant
Alien Control Organism
7Biological Control as a Lottery
- Runaway importation rates
- Monitoring and evaluation gap
McEvoy and Coombs 2000
8Biocontrol of Leafy Spurge
9Practicing biocontrol as a lottery can lead to
revenge effects (McEvoy and Coombs 1999)
- Scarce resources are diverted from more
profitable alternatives for managing pests - One control organism undermines another, more
effective control organism, leading to increase
in pest density - One pest is replaced by another pest that is even
harder to control - Control organisms introduced to promote
environmental and economic health end up
undermining it by harming non-target organisms
10Questions to Answer Before Releasing New
Organisms Into the Environment
- Are new organisms necessary? What is the severity
of the problem? - Are they effective? How effective is the proposed
solution to the problem? - Are they safe? Will control organism harm other
plants?
11Are Control Organisms Likely to Be Effective?
- Critical Attributes. Species with desirable
biological properties can be selected based on
expert intuition, data bases, and mathematical
and experimental models. - Targeted disruption of pest life cycles. Using
field studies and math models to identify which
life-cycle transitions and pathways contribute
most to population growth, which are most easily
disrupted, and using this information to improve
targeting of pest vulnerabilities - Combinatorial Ecology. Coordinated manipulation
of disturbance, plant competition, and natural
enemy regimes
12Insects for Control of RagwortSenecio jacobaea
(Asteraceae)
1960 Tyria jacobaeae (Lep Arctiidae) Cinnabar moth
1966 Botanophila seneciella (Diptera Anthomyiidae) Ragwort seed fly
1970 Longitarsus jacobaeae (Coleoptera Chrysomelidae) Ragwort flea beetle
13Traditional Paradigm Focus on Level and
Stability of Pest-Enemy Equilibrium
14Ragwort Biocontrol
15Ragwort Biocontrol by the Numbers
Forbs
Grasses
McEvoy et al 1991
16Biocontrol of Klamath Weed in CA Huffaker and
Kennett 1959
Total Forage
Percentage Cover
Other Weeds
Year
17Lingering UncertaintiesCinnabar Moth Friend or
Foe?
- Necessary. Is cinnabar moth necessary for ragwort
control? - Effective. Is it effective in controlling the
target host? - Safe. Is it a threat to nontarget species?
18Control Value of Ragwort Seed-Head Fly
- Fly oviposition and ragwort flowering are not
well synchronized - Early, aggregated attack by the fly means 70 of
flowering heads escape attack
19General Questions
- Patterns in system dynamics. What are the
patterns in the dynamics of weed biocontrol
systems? - Regulatory mechanisms. How are these systems
regulated? - Response to perturbation. How does the system of
interactions respond to perturbation?
20Combinatorial EcologyFood Webs and Driving Forces
C
- Disturbance
- Colonization
- Local interactions (successional development)
H
P
R
21Hypotheses
- The Activation Hypothesis is that localized
disturbances and buried seed combine to create
incipient weed outbreaks. - The Inhibition Hypothesis is that natural enemy
attack and interspecific plant competition
combine to oppose increase and spread of
incipient weed outbreaks. - The Stability Hypothesis is that the balance in
activation and inhibition leads to a general
condition of local instability and stable average
concentration of the pest.
22Goals of Demographic Analysis(McPeek and Kalisz
1993)
- Population growth. Estimate population growth
rate and project future population dynamics - Stable stage distribution and reproductive
values. Understand and project population
structure and contributions of different types of
individuals to future reproduction - Sensitivity and Elasticity. Understand
contributions of each age or stage class to
overall population growth rate and fitness
23Design of LTRE
Synthesis
VITAL RATES
POPULATION STATISTICS
T1
E1
A(1)
VITAL RATES
POPULATION STATISTICS
TN
A(N)
EN
Matrix
Treatment
Effect
Analysis
24Matrix Population Model
Life Cycle Graph Age and Stage
Projection Matrix M
D J1 J2 A
D a 0,0 0 0 a 0,3
J1 a 1,0 0 0 a 1,3
J2 0 a 2,1 a 2,2 0
A 0 a 3,1 a 3,2 a 3,3
J2
J1
A
D
Nt1 M Nt At SSD Nt1/Nt ?
Time scale 1 yr
25Life Table Response Experiment (LTRE)Experimental
Design
- 2 Disturbance Times (Fall 86, Spring 87)
- 3 Plant Competition Levels (Removed, Clipped,
Unaltered) - 2 Cinnabar Moth levels (Present, Absent)
- 2 Flea Beetle Levels (Present, Absent)
- 4 Blocks
- 96 experimental units
26Treatment Effects on Population Growth
27Prospective and Retrospective Analysis
External Forces Life Cycle Transitions Population Growth Rates
?ij ?
28Elasticity Analysis
Elasticities sum to 1.0 and represent the
proportional contribution of each element to ?
29Elasticity
Percentage of total elasticity associated with
each life cycle transition
Perennial N 8 subpopulations
Biennial N 24 subpopulations
11
50
14
J1
A
14
37
50
24
30Treatment Effects
X
Plant Competition
Flea Beetle
Cinnabar Moth
X
J2
J2
J2
X
X
X
X
X
J1
J1
A
J1
A
X
A
X
31A Sound Control Strategy for Control of Ragwort
Should
- 1) favor the ragwort flea beetle over the
cinnabar moth - 2) promote plant competition
- 3) reduce the intensity and frequency of
disturbance
32Conclusions Regarding Control Effectiveness
- Driving forces of disturbance, colonization, and
local interactions (competition and herbivory) - Parsimonious prescription. Control can be
achieved using fewer natural enemies by
coordinated manipulation of disturbance,
competition, and natural enemy regimes
33Specific Models Have Practical Benefits (Barlow
1999)
- Outcome of introduction predicting the outcome
and success of a specific introduction - Agent selection aiding in the selection of the
most appropriate agent - Predicting the impact of exotic agents on
ecosystems and non-target species - Understanding of the processes involved
- Critical data assisting in the identification
and interpretation of critical field data
34Prickly Pear in South AfricaLogistic Pattern
35Opuntia aurantiaca and Dactylopius austrinus in
South AfricaPopulation Cycles
Moran and Zimmerman 1991
36Insects for Control of Sesbania punicea in South
Africa
Species Resources Treatments Treatments Treatments Treatments
Species Resources A-C D-F G-L M-P
Trichapion lativentre Flower buds x x x x
Rhyssomatus marginatus Developing seeds x x
Neodiplogrammus quadrivittatus Trunk and stems x x
37Number and Identity of Species for Sesbania
Control
Hoffman and Moran 1998