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Migration

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Title: Migration


1
Migration
  • Peter B. McEvoy
  • Insect Ecology
  • Ent 420/520

2
Objectives
  • Measure and model migratory movement in relation
    to habitat persistence
  • Distinguish migration from other forms of
    movement
  • Place movement in context of life histories
  • Identify physiological controls
  • Appreciate role of Mathematical Theory
  • Discuss causes and consequences of polymorphism
    in migratory capacity
  • Illustrate role of migration in pest outbreaks
  • Illustrate role of movement and spatial
    heterogeneity in Population Dynamics

3
Importance of Migration to Many Fields
  • Ecology changes in population size, founding of
    new populations, outcome of species interactions
  • Behavior- movement a process involving decisions
    such as when to move, what direction to take, and
    when to stop
  • Physiology environmental variables that induce
    migration (photoperiod, population density, food
    quality, and weather patterns) and neural and
    hormonal mechanisms that process those cues
  • Evolutionary Biology- an adaptation correlated
    with spatial and temporal patterns of habitat
    suitability
  • Population Genetics genetic differences in
    tendency to move may constitute polymorphism
    movement often results in gene flow, and gene
    flow may counteract tendency toward local genetic
    differentiation
  • Applied Entomology techniques for measuring,
    predicting, controlling movement

4
Migrant Pests
  • Potato leaf hopper Empoasca fabae

Six-spotted leafhopper Macrosteles fascifrons
(HOMOPTERA CICADELLIDAE)
Arrive suddenly, often in vast numbers, in
northern regions where breeding is not active.
Apparently migrate in spring from lower
Mississippi Valley breeding grounds, aided by
southerly winds.
5
Painted LadyVanessa cardui
Photos by Mario Maier
  • Migrations originate in the deserts of Mexico,
    where heavy winter rains trigger growth of larval
    food plants.

6
Persistent Unanswered Questionsabout Migrants
  1. What proportion of northern populations accounted
    for by immigration vs. local breeding?
  2. Does a return southward migration occur in the
    fall?
  3. What are the distances travelled by individual
    migrants?
  4. Is northward spread achieved by a single
    generation or by series of northward advances by
    separate generations?

7
U Fla book of records Longest Migration. desert
locust, Schistocerca gregaria (Acrididae)
migrated westward across the Atlantic ocean 4500
km during the fall of 1988
8
Importance of Migration to Ecology
  • Habitat. Essential in temporary habitats,
    retained in persistent habitats
  • Stability. Can stabilize population fluctuations
    and species interactions
  • Gene flow. Determines gene flow and genetic
    structure of populations
  • Resource allocation and life cycle. Migration a
    costly part of total resource allocation
    resource limitation may require a trade-off
    between migration and reproduction

9
Evolving Dispersal
Weighing benefits and costs
Trends in Ecology and Evolution, 2000, 1515-7
10
Literature on wing polymorphism and migration
  • Southwood 1962
  • JS Kennedy
  • Johnson 1969
  • Dingle 1972, 1985
  • Harrison 1980, Hardie and Lees 1985, Pener 1985,
    Roff 1986
  • Zera and Denno 1997 Ann Rev Entomol 42207-231

11
Distinguishing Features of Migration as a form of
Movement
  1. Persistent
  2. Straightened-out track
  3. Undistracted by resources that would ordinarily
    halt it
  4. Distinct departing and arriving behaviors
  5. Energy is reallocated to sustain it

12
Example of active dispersalGreat Southern White
Butterfly(Ascia monuste Pieridae )
  • Strong control over flight within the boundary
    layer

13
More nearly passive dispersal Black Bean Aphid
(Aphis fabae)
  • Passive dispersal flies above boundary layer
    where its air speed swamped by wind speed
  • Element of active control in entry, maintenance,
    and exit
  • Life cycle includes alternation between winged
    and wingless forms

Alate or winged
Aptera or wingless
  • Alate formation can be suppressed by increasing
    temperature, increased by crowding, suppressed by
    ant attendance, increased by enemies

14
Cabbage Aphid Brevicoryne brassicae (Homoptera
Aphididae)
Population begins with a small proportion of
alatae at low population densities, and the
proportion increases as population grows. Not
reversible, but instead local colony eventually
disappears
15
Spring and Fall Migration of the Monarch Butterfly
16
Relationship Between Dispersal and Life History
Parameters (Dingle 1972)Outline of Study
  1. Individual should have high reproductive value
    when it migrates
  2. Mechanisms that enforce delay in reproduction
    until after migration (photoperiod)
  3. Effect of environment and selection on flight
    tendency (temperature, diet, photoperiod,
    genetics)
  4. Population growth potential of migrant and
    post-migrant

17
Concept Alert!
  • Natural selection differential change in
    relative frequency of genotypes due to
    differences in the ability of their phenotypes to
    obtain representation in the next generation
  • Heritability the fraction of variance in a
    given characteristic of a population that is due
    to genetic variation in the population
  • Fitness the relative rate by which the
    frequency of a given genotype is increased each
    generation by selection

18
Concept Alert!
  • r the intrinsic rate of increase the fraction
    by which a population changes in size in each
    unit of time
  • R the net reproductive rate the average number
    of females produced in the next generation by
    each female in the present generation
  • ? ln r the finite rate of increase the
    fraction by which a population changes in size in
    each unit of time

19
Concept Alert!
  • vx reproductive value the expected number of
    offspring contributed to future population growth
    by female of age (or stage) x

20
A Migrant Milkweed Bug    Oncopeltus
fasciatus(Lygaeidae)
  • Tropical genus of milkweed bugs
  • Range of 1 sp in genus, O. fasciatus, extends
    into temperate zone
  • Reproduces on developing pods
  • Short days (1212 LD) trigger migration southward

21
Nonmigrant relativeSmall Milkweed Bug Lygaeus
kalmii
22
Table 1. Effect of environment (temperature,
starvation, photoperiod) and selection on fight
in milkweed bug Oncopeltus fasciatus
Conditions Conditions Sample size Number flying gt30 min Percent flying
(1) 168 LD 23oC Parent 311 74 23.8
(2) 168 LD 23oC Offspring 47 30 63.8
(3) 168 LD 27oC 98 10 10.2
(4) 1212 LD 24oC 54 38 70.4
(5) LD 168 LD Starved 3 days 23oC 148 70 47.3
Contrast 1 and 3 Effect of temperature 1 and 5
Effect of starvation 1 and 4 Effect of
photoperiod 1 and 2 Effect of selection
Dingle 1972
23
Table 2. Effect of day length, temperature on
intrinsic rate of increase in Oncopeltus
fasciatus
Conditions Conditions Age 1st reproduction Increase per day r Doubling Time
(1) 168 LD 27oC 47 0.0810 8.90
(2) 1212 LD 27oC Migrant 61 0.0593 12.03
(3) 168 LD 23oC 63 0.0499 14.24
(4) 1212 LD 23oC Migrant 95 0.0369 19.13
Compare 1 and 2 Effect of Photoperiod 3 and 4
Effect of Photoperiod 1 and 3 Effect of
Temperature 2 and 4 Effect of Temperature
Dingle 1972
24
Gadgils TheoryMathematical Theories of Dispersal
  • Conceptualizes an array of habitat patches which
    vary in carrying capacity ki(t)
  • Examines influence of variation in the k's on
    magnitude of dispersal and sensitivity to
    crowding
  • When k's constant or k's vary in phase, selection
    will favor a low magnitude of dispersal, but
    higher sensitivity to crowding
  • When k's vary out of phase, selection favors
    increasing magnitude of dispersal and decreasing
    sensitivity of density response

25
Empirical Patterns Relation between flight
ability and habitat in water beetles in England
Permanent Temporary Permanent Temporary Permanent Temporary Permanent Temporary Permanent Temporary
Southwood 1962 Rivers springs Lakes, tarns, canals Brackish water, peat bogs Ponds, ditches Artificial ponds, gravel pits, cattle troughs
Able to fly 3 10 30 27 24
Variable 6 13 14 15 8
Unable to fly 13 7 7 2 0
How reliable are inferences from observational
data?
26
Dispersal Polymorphism in Insects
  1. Taxonomic Occurrence in insect orders (next
    slide)
  2. Importance for understanding population dynamics
    and species interactions, life history
    evolution,and physiological basis of adaptation
  3. Temporal Hypothesis. Habitat persistence selects
    for reduced dispersal capability (Denno)
  4. Spatial Hypothesis. Habitat continuity/isolation
    selects for reduced dispersal capability (Dixon)
  5. Constraints. Fitness trade-off between dispersal
    and reproduction results from trade-off in
    allocation of internal resources

27
Taxonomic distribution and types of dispersal
polymorphism
  • Orthoptera
  • Psocoptera
  • Thysanoptera
  • Homoptera
  • Heteroptera
  • Coleoptera
  • Diptera
  • Lepidoptera
  • Hymenoptera

Forms of dispersal polymorphism Wing
polymorphism Flight muscle polymorphism
28
Dispersal capability of wing forms
  1. Migrants. Long-winged form (macropter) only
    form capable of flight, primarily responsible for
    escaping deteriorating habitats and colonizing
    new ones
  2. Genetics, environment. Wing morph can result from
    genetic, environmental, or genetic x
    environmental variation
  3. Genetics. Polygenic control more common in
    Orthoptera, Demaptera, Homoptera, Heteroptera
    single-gene control in Coleoptera and Hymenoptera.

29
Life History Evolution
  • Traits migration, diapause, age at first
    reproduction, fecundity linked in syndrome
  • Trade offs between dispersal and fitness
    components for females
  • Fecundity lower in macropters (grasshoppers,
    crickets, planthoppers, aphids, waterstriders and
    veliids, water boatmen, seed bugs, pea weevils)
  • Reproduction delayed in migratory forms of
    grasshoppers, crickets, aphids and planthoppers,
    waterstriders, true bugs, and beetles
  • Trade off between dispersal and fitness for males
    cost of reproduction generally lower in males

30
What behaviors may partially compensate for
inherently lower reproduction in macropters?
  1. Selective colonization of nutrient-rich resources
  2. Large body size and correlated fecundity
  3. Trading off small egg size for increased egg
    number
  4. Histolyis of wing muscles upon arrival in new
    habitat with energy reallocation to reproduction

31
WHAT DETERMINES WING FORM?
  • A hormonally controlled developmental switch
    that responds to environmental cues
  • CROWDING
  • HOST PLANT CONDITION
  • TEMPERATURE
  • PHOTOPERIOD
  • So, depending on the conditions it experiences as
    a nymph, an individual will molt into either a
    brachypter (short-winged) or macropter
    (long-winged).

32
Physiological Control of Wing Polymorphism
  1. Hormones. Endocrine regulation of morph
    development based on level of JH and ecdysone
    shown for the case of one cricket species
  2. Environmental cues such as crowding, host plant
    condition, temperature, and photoperiod influence
    wing form
  3. Sensitive stage can occur prenatal, postnatal,
    middle (e.g. planthoppers), late stages (e.g.
    crickets)

33
PLANTHOPPERSDELPHACIDAE
Macropter
Brachypter
Study system provides the first rigorous
assessments of the relationship between dispersal
and habitat persistence
34
Migration in Relation to Habitatfor the salt
marsh planthopper Prokelisia marginata
  1. Emerge winter-spring high marsh
  2. Migrate spring-summer to low marsh
  3. Thrive in Summer low marsh
  4. Return migration in Fall to high marsh

35
Fig 1. Macroptery decreases as habitat
persistence increases for 35 spp planthoppers
Test of hypothesis requires operational
definitions of variables dispersal capability
and habitat persistence
Females
Males
Relationship is nonlinear
36
Negative relation between dispersal and habitat
persistenceSummary of Evidence
  1. Interspecific contrasts. For 35 species of
    planthoppers inhabiting low-profile vegetation,
    there was a significant, negative, nonlinear
    relationship between dispersal capability (
    macroptery) and the persistence of their habitats
    (maximum number of generations attainable)
  2. Phylogenetically-independent contrasts. Same
    result for phylogenetically independent contrasts
    between congeners
  3. Intraspecific contrasts. Negative relationship
    between dispersal capability and habitat
    persistence found
  4. True for 2-D habitats, but not for 3-D
    habitats, e.g. wing polymorphic and flightless
    species tend to be rare in trees

37
Fig 2. Effect of Crowding Macroptery increases
with rearing density for Prokelisia marginata and
P. dolus
P. marginata Temporary habitat Highly migratory
Males gt Females
P. dolus Persistent habitat Less migratory Males
Females
Summary of Effects Species Differences between
species Gender Differences between male and
female with species Gender x Species Gender
difference varies by species
38
Fig 3. Macroptery Response to Rearing Density for
5 Other planthoppers All species are migratory
and occur in temporary habitats except M.
fairmairei, which resides in persistent grasslands
  • Varies by
  • Species
  • Gender -
  • Gender x Species

39
Genetic variation within a single species?
macroptery reponse to rearing density for P.
marginata from (A) temporary (NJ) and (B)
persistent (FLA) habitats
What constitutes appropriate and adequate
replication in this comparison?
Temporary (NJ)
Persistent (FLA)
40
Male Bias in macroptery found in habitats of low
persistenceMales are more likely than females to
remain in temporary habitats
Null expectation
males/females
41
Gender differences
  1. Macroptery increases with local density Females
    often more sensitive to increasing density than
    males. Why?
  2. Cost of reproduction higher in females than
    males. Why?
  3. Trade off between reproduction and dispersal well
    documented in females. How?
  4. Similar trade off can occur in males. How?
  5. Dual role of wings in colonization and mate
    location. In temporary habitats, wings may be
    retained in males to locate females at low
    colonizing densities. How might we separate
    contributions of migration to mating and
    colonizing ability?

42
Conclusions
  • Separating influences of environment and
    ancestry Habitat persistence has influenced
    migration independently of common ancestry
  • Interactions of factors Habitat persistence also
    influences the wing-form response of planthoppers
    to crowding.
  • Flight reflects multiple selective forces
    Density wing-form responses of planthoppers
    reflect two density-related advantages of flight
    Habitat escape and Mate location.

43
Summary and Future Directions
  • NOW We have rigorous assessments of
  • Relationship between habitat stability and
    dispersal capability
  • Trade-off between flight capability and
    reproduction (including physiological basis)
  • Endocrine control of flight capacity in a
    wing-dimorphic insect (cricket)
  • FUTURE We need further investigation of
  • Trade-off between flight capacity and
    reproduction in males
  • Endocrine control known only for one species
  • Ecological and physiological mechanisms in same
    species
  • Fates of migrants and nonmigrants, reliability of
    wing polymorphism as index of migration
  • Migration in the context of population dynamics
    at landscape scale

44
Migration in the Context of Population Dynamics
  1. Several species of forest insects exhibit
    outbreaks
  2. Progress being made on temporal patterns and
    underlying mechanisms (Turchin 1990 Berryman
    1996)
  3. Outbreaks can also exhibit a sptio-temporal
    pattern known as traveling waves (Johnson,
    Bjornstad, Liebhold 2004 Ecol Letters 7967-974)

45
Landscape Ecology in a Nutshell
  1. The field of landscape ecology addresses how
    landscape mosaics -- i.e. the spatial
    interspersion of favorable habitats ('patches')
    and non-favorable habitats ('matrix) - affect
    ecological processes (Turner et al. 1989, Wiens
    et al. 1993).
  2. The idea is that the proximity of favorable
    habitats, and/or permeability (Stamps et al.
    1987) of any matrix habitat, will enhance the
    exchange of migrants (connectivity) between
    such habitats. Thus persistence of sink
    populations can be enhanced by subsidies from
    source habitats, the growth of satellite
    populations fueled by waves of immigrants.
  3. Previous studies suggest that landscape
    heterogeneity and fragmentation can affect the
    dynamics of pest populations (Shigesada et al.
    1986, Roland 1993).

46
Herbivore population dynamicslarch budmoth in
Swiss Alps(Zeiraphera diniana Gn.)
  • Remarkably regular 8-10 yr cycle
  • Covering 5 orders of magnitude per cycle
  • O.N. Bjørnstad, M. Peltonen, A. M. Liebhold, W.
    Baltensweiler 2002 Science 2981020-1023.

47
Time series of larch budmoth larval density
(average of 5 permanent sites) and defoliation
(all Alps).
Damage can be used as a surrogate for insect
density Phase 8-9 yr cycle Amplitidue 5
log-cycles
This figure shows that defoliation time-series
very closely tracks time-series in actual
population density and thus serves as an adequate
proxy to population density
48
Trophic hypotheses for Larch BudwormTop-Down or
Bottom-Up or Other?
  • Food quality defoliation ?low quality needles
    (higher fiber, lower N) ?reduced larval survival
    and female fecundity
  • Pathogens granulosis virus
  • Parasitoids parasitism rates low (10-20) at
    peak LBM to high (90) 2-3 yr after peak
  • Polymorphic Fitness hypothesis dark morph
    (deciduous larch) increases during population
    increase and light morph (evergreens) increases
    during population collapse
  • Other hypotheses host quantity, predators
  • Turchin concludes plant quality and parasitism
    interact in their effects

(Turchin)
49
Color pattern varies during the cycle
Are evolutionary changes in budworm population
contributing to cycles in dynamics?
  1. Dark vs Light. The larch form caterpillars are
    usually dark, but during the decline phase,
    lighter forms appear.
  2. Selection vs gene flow. May reflect gene flow
    from the pine form of the moth, or selection
    within the larch form population
  3. Cause vs consequence. Changes in morph frequency
    may be a consequence of changes in density,
    rather than a cause of changes in density

50
Are changes in host quality (leaf fiber content)
contributing to budworm dynamics?Plant Quality
and Larch Bud Moth Performance
Larval mortality increases with fiber content of
needles
Pupal mass decreases with fiber content of needles
51
Larch Budmtoh Zeiraphera diniana in European
AlpsSpatio-Temporal Pattern of Dynamics
Wave travels from 219.8 to 254 km/yr in NE direct
(varying with method of estimation)
  • http//www.sandyliebhold.com/pubs/science_DC1/

52
Epicenter Hypothesis
  1. Regional outbreaks begin in specific foci and
    then spread into adjoining areas
  2. Example include spruce budworm, gypsy moth, and
    mountain pine beetle
  3. Commonly claimed that outbreak starts in habitats
    of high quality (i.e. where population growth
    rate is highest) and spread via dispersal to
    elevate pest densities in surrounding suboptimal
    habitats to initiate secondary outbreaks
  4. There is evidence contradicting this
    hypothesisforcing a modification of the
    epicenter hypothesis

53
Spatial Version of Nicholson-Bailey Model
Capatures nonlinear parasitoid-host interaction
  1. Spatially-distributed population models predict
    complex spatial dynamics, such as spiral waves
    and spatial chaos, as a result of trophic
    interactions
  2. Bjornstad et al (2002) demonstrate the existence
    of waves in Central European larch budmoth
    (Zeiraphera diniana Gn.) outbreaks
  3. Waves travel toward the northeast-east at 210 km
    per year later revised to 254 km per year
  4. A theoretical model involving a moth-enemy
    interaction predicts directional waves, but only
    if dispersal is directionally biased or habitat
    productivity varies across the landscape. Later
    revised to emphasize habitat geometry and
    dispersal.
  5. Study confirms that nonlinear ecological
    interactions can lead to complex spatial dynamics
    at a regional scale

54
Nicholson-Bailey Type Models
  • Discrete-time models designed mainly for annual
    insects with one generation per year and no
    overlap in generations.
  • Nt1 Nt ? g(Nt) f(Nt,Pt)
  • Pt1 c s Nt 1 - f (Nt,Pt)
  • Nt, Nt1, and Pt, and Pt1 represent the host and
    parasitoid population densities in successive
    generations, respectively
  • ? is the geometric growth rate of the host (which
    can remain constant or change as a function of
    host density according to density dependent
    function ? g(Nt)
  • c is the number of parasitoids produced for each
    host individual attacked (the "numerical
    response" of the parasitoid)
  • s is the proportion of parasitoid progeny that is
    female
  • f(Nt,Pt) gives host survival with respect to
    parasitoid and host densities and can be varied
    to reflect variation in parasitoid foraging
    behavior

55
Outbreaks originate (left) in areas of high
connectivity (right)
56
Vector Plot showing local relative speeds and
directions
  • Vector plot indicating local relative speeds and
    directions of larch budmoth wave movement across
    the Alps. The circles indicate two-wave
    epicentres.

57
Summary LBM Study
  1. Travelling waves in cycling populations highlight
    the importance of migration in population
    dynamics
  2. Waves in LBM outbreaks originate from two
    epicenters, both located in high concentrations
    of favorable habitat
  3. Movement in relation to ecosystem texture may be
    responsible for travelling waves
  4. A tri-trophic model of LBM show landscape
    heterogeneity (specifically gradients in density
    of favorable habitat) sufficient to induce waves
    from epicenters
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