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Impact of Lake Organisms on Terrestrial Systems

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Title: Impact of Lake Organisms on Terrestrial Systems


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Impact of Lake Organisms on Terrestrial Systems
  • By Vik Walia

3
Outline
  • 1. Introduction
  • 2. Article 1 Trophic Cascades
  • 3. Article 2 Indirect Effects of Aquatic
    Insects on Terrestrial Insects
  • 4. Future Directions

4
Introduction
  • So What are trophic cascades anyways?
  • - Interactions between trophic levels
    (decomposer, producer, herbivore, predator) that
    result in inverse patterns in abundance or
    biomass across more than one trophic link in a
    food web

5
Example Consider a 3-level food chain
  • Predators can decrease herbivore
    abundance/biomass, indirectly benefiting the
    plants (the producers)

6
Article 1 Trophic Cascades Across Ecosystems
  • Purpose Show that Fish indirectly facilitate
    terrestrial plant reproduction through cascading
    trophic interactions across ecosystem boundaries

7
4 Aspects were tested to prove hypothesis
  • Fish limit the size and abundance of larval
    odonates
  • Correlation of fish presence with pollinator
    visitation
  • Whether effects of fish indirectly influenced
    plant reproductive output
  • Pollinator visitation would be lower near
    fish-free ponds for 2 reasons
  • Adult dragonflies predate on pollinators
  • Pollinators behaviourally avoid foraging near
    adult dragonflies

8
Interaction web showing the pathway by which fish
facilitate plant reproduction
Solid arrows direct interactions Dashed arrows
indirect interactions Sign expected direction
of the direct or the indirect effect
9
How do Fish play a role?
  • Larval stages of many freshwater organisms (i.e.
    dragonflies frogs) are vulnerable to a suit of
    aquatic predators (i.e. fish), whereas the adult
    stages are important consumers in terrestrial
    habitats
  • Thus, the intensity of predation experienced by
    juvis in the aquatic habitat can be predicted to
    influence (indirectly) the intensity of predation
    imposed in turn by adults in terrestrial habitats

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The Site U of Florida
  • 18 permanent ponds that differed in whether or
    not they have fish
  • Chose 8 ponds (4 with fish, 4 without)
  • There was no systematic differences between the
    ponds

11
4 Aspects were tested to prove hypothesis
  • Fish limit the size and abundance of larval
    odonates
  • Correlation of fish presence with pollinator
    visitation
  • Whether effects of fish indirectly influenced
    plant reproductive output
  • Pollinator visitation would be lower near
    fish-free ponds for 2 reasons
  • Adult dragonflies predate on pollinators
  • Pollinators behaviourally avoid foraging near
    adult dragonflies

12
How did they test it?
  • Surveyed dragonfly abundances in and near
    fish-containing and fish-free ponds

13
Results
  • sorted dragonfly species into 3 size categories
    S, M, L
  • Graph a Size distribution of dragonflies
  • in ponds with fish, more M and L larval
    individuals and fewer S larval individuals
  • Graph b Abundance of dragonflies
  • abundance of adult dragonflies was lower near
    ponds with fish than without

14
4 Aspects were tested to prove hypothesis
  • Fish limit the size and abundance of larval
    odonates
  • Correlation of fish presence with pollinator
    visitation
  • Whether effects of fish indirectly influenced
    plant reproductive output
  • Pollinator visitation would be lower near
    fish-free ponds for 2 reasons
  • Adult dragonflies predate on pollinators
  • Pollinators behaviourally avoid foraging near
    adult dragonflies

15
How did they test it?
  • Observed pollinator visitation on the most common
    shoreline flowering plant, Hypericum fasciculatum
    (aka St. Johns-Wort) in and near fish-free ponds
    and those containing fish

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Results
  • Total number of pollinator visits to St.
    Johns-Wort was higher near ponds with fish
  • Bars represent groups of pollinators
  • black bars Diptera (flies)
  • grey bars Lepidoptera
  • white bars Hymenoptera (bees)
  • St. Johns-Wort has evolved traits that attract
    bees, therefore
  • bees are more effective at pollinating than
    flies
  • Why does this matter?
  • - effect is magnified

17
4 Aspects were tested to prove hypothesis
  • Fish limit the size and abundance of larval
    odonates
  • Correlation of fish presence with pollinator
    visitation
  • Whether effects of fish indirectly influenced
    plant reproductive output
  • Pollinator visitation would be lower near
    fish-free ponds for 2 reasons
  • Adult dragonflies predate on pollinators
  • Pollinators behaviourally avoid foraging near
    adult dragonflies

18
How did they test it?
  • Performed pollen supplementation experiments to
    determine degree to which plant seed production
    was limited by pollen receipt at each pond
  • How do pollinators drive plant population and
    community dynamics?
  • If they dont visit too often, plants will
  • fail to reproduce
  • produce fewer seeds
  • produce lower quality seeds

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Results
  • Plants near fish-free ponds were more than 2X as
    pollen limited than plants near ponds with fish
  • To make sure that the result they were getting
    was validthey tested another species of plant
    called Saggitaria latifolia
  • also showed an increased number of pollinator
    visitations and therefore increased plant
    reproductive output at ponds with fish
  • This indicates that the indirect effect of fish
    upon plant reproductive success is general

20
4 Aspects were tested to prove hypothesis
  • Fish limit the size and abundance of larval
    odonates
  • Correlation of fish presence with pollinator
    visitation
  • Whether effects of fish indirectly influenced
    plant reproductive output
  • Pollinator visitation would be lower near
    fish-free ponds for 2 reasons
  • Adult dragonflies predate on pollinators
  • Pollinators behaviourally avoid foraging near
    adult dragonflies

21
How did they test it?
  • Over a 7-day period, they observed several
    predation events by 2 species of dragonflies
    (Anax junius, Erythemis simplicicollis) known to
    attack large insect species including pollinators

22
Results
Found that 4 out of every 8 observed predation
events were on pollinators (bees, moths, and
flies)
23
4 Aspects were tested to prove hypothesis
  • Fish limit the size and abundance of larval
    odonates
  • Correlation of fish presence with pollinator
    visitation
  • Whether effects of fish indirectly influenced
    plant reproductive output
  • Pollinator visitation would be lower near
    fish-free ponds for 2 reasons
  • Adult dragonflies predate on pollinators
  • Pollinators behaviourally avoid foraging near
    adult dragonflies

24
How did they test it?
  • Put cages around naturally occurring species of
    St. Johns-Wort near a pond with fish
  • mesh size allowed for free visitation by most
    pollinators and precluded escape of 1 species of
    dragonflies (E. simplicicollis)

25
Results
  • Fewer visitors entered cages containing
    dragonflies than control cages (used a paired
    t-test to quantify t -4.2, p 0.02)
  • Visitors that had entered cages with dragonflies
    forged on fewer flowers than visitors that
    entered cages not containing dragonflies (t
    -3.8, p 0.009)
  • Resulted in H. fasciculatum flowers receiving
    fewer overall visits in the presence of a
    dragonfly

26
Putting It ALL Together
  • Strong linkages between consumers in aquatic
    terrestrial communities are not limited to this
    special case
  • Many terrestrial predators, herbivores have
    larval aquatic stages
  • Thus, aquatic predators might have a variety of
    consequences for interactions in neighboring
    terrestrial ecosystems

27
Lets not forget
  • Similarly, many organisms (ex. Salamanders) with
    terrestrial life-stages are important aquatic
    predators
  • Thus, interactions in terrestrial ecosystems can
    cascade into aquatic ecosystems as well

28
Article 2 Indirect effect of aquatic insect
emergence on terrestrial insect population
through by birds predation
  • Purpose determine the effect of birds,
    subsidized by aquatic emergence, on the insect
    herbivores in a riparian deciduous forest

29
Background
  • Most systems have a heterogeneous pattern of
    resource distribution and this gives rise to a
    heterogeneous distribution of predators
  • When distribution of 2 prey types differs, the
    distribution of predators is determined by the
    1st prey species and predation intensity on the
    2nd prey species can be indirectly affected by
    the distribution of the first
  • This suggests a heterogeneous occurrence of
    indirect interaction between prey species sharing
    a common predator

30
How does this relate?
  • In a forest-stream ecotone
  • Forest birds depend highly upon aquatic insects
    emerging from the stream early in spring
  • Before spring leafing
  • Terrestrial productivity 0
  • Stream productivity is at its highest
  • Why? More exposure to sunlight
  • This asynchrony is responsible for a significant
    seasonal energy flow from stream to forest

31
Top-down control of herbivorous insects by birds
  • Ex. Marukami (1999)
  • Showed that a population of leaf rolling
    Lipdoptera larvae on Japanese Lilac were
    controlled by birds
  • Japanese lilac break bud earlier that other trees
  • Thus, the foraging of insectivorous birds was
    concentrated on the Japanese lilac in early spring

32
What did they predict? Hypothesis!
  • An emerged aquatic subsidy supports a denser bird
    population along a stream compared with that of
    an upland forest
  • Thus, there would be a decrease in herbivore
    population on riparian vegetation in early spring

33
What did they use to test the hypothesis?
  • Analyzed the distribution and abundance of birds
    on riparian and upland forest
  • Assessed the degree by which forest birds are
    subsidized by emerged aquatic insects
  • Addressed the manner in which the aquatic
    subsidies affect bird distribution within a
    forest and hence the herbivore population

34
How did they test it?
  • Bird Observations
  • 4 dominant insectivorous bird species were
  • Great tits, Marsh tits, Narcissus flycatchers,
    Willow Warblers
  • Visiting frequencies to each plot and prey types
    were recorded every other day for a total of 10
    days
  • Narcissus flycatchers did not utilize leaf
    rollers on lilac trees throughout the study
    period and were excluded from further
    investigation

35
Results
  • Bird visitation rates to riparian plots were
    greater than those to upland forest for great
    tits and crowned willow warblers
  • No significant difference for marsh tits

36
Results
  • Riparian Plots
  • all 3 bird species frequently utilized aquatic
    insects emerging from the stream (30-60 for each
    bird species)
  • leaf rollers also utilized by all 3 bird species
    (rate of 15-50)
  • Upland Plots
  • birds rarely utilized insects emerging from
    stream
  • leaf rollers were utilized 30-45 as well as
    other terrestrial insects
  • Although rate of leaf roller utilization was low
    in riparian forest, amount of overall predation
    on leaf rollers was much higher in riparian
    forest because there was a greater bird
    population and therefore a greater visitation
    frequency

37
What did they use to test the hypothesis?
  • Analyzed the distribution and abundance of birds
    on riparian and upland forest
  • Assessed the degree by which forest birds are
    subsidized by emerged aquatic insects
  • Addressed the manner in which the aquatic
    subsidies affect bird distribution within a
    forest and hence the herbivore population

38
How did they test it?
  • Abundance of flying insects was surveyed by a
    malaise trap
  • Trap was set during the middle of the study
    period
  • Collected arthropods were preserved in 70
    ethanol and sorted into terrestrial and aquatic
    insects, component species being identified to
    order
  • Biomass of each order and family was measured as
    wet mass and the dry mass was estimated
    subsequently
  • Insect masses were then compared between riparian
    and upland forests separately for terrestrial and
    aquatic insects

39
Results
  • Biomass of aquatic and terrestrial insects in
    riparian and upland forests caught by malaise
    trap (vertical bars indicate std. error)
  • no significant difference occurred in
    terrestrial prey biomass between riparian and
    upland forests (P0.786)
  • aquatic prey biomass was much higher in riparian
    forest (P0.013)

40
What did they use to test the hypothesis?
  • Analyzed the distribution and abundance of birds
    on riparian and upland forest
  • Assessed the degree by which forest birds are
    subsidized by emerged aquatic insects
  • Addressed the manner in which the aquatic
    subsidies affect bird distribution within a
    forest and hence the herbivore population

41
How did they test it?
  • Bird exclusion experiment
  • 5 randomly selected trees in 3 riparian and 3
    upland plots were enclosed by cages of 15mm nylon
    mesh net that allowed most insects but no birds
    to pass through
  • additional 30 non-enclosed tress (15 from
    riparian and 15 from upland) were selected to
    controls
  • of 3 dominant leaf roller species per shoot was
    calculated at the end of the experiment by
    counting the numbers of leaf rolls and shoots on
    each individual tree
  • effects of bird removal on the of leaf rollers,
    treatment and site (riparian or upland) being the
    factors were detected by 2-way ANOVA

42
Results
  • Impacts of birds differed among the leaf roller
    species
  • H. foederatana s decreased because of
    predation by birds, particularly in riparian
    forest plots as shown by the significant effects
    of both treatment and site with the interaction
    also being significant
  • no significant bird effects found on A. viola or
    Z. corpulentana leaf roller s
  • Indicates that the latter 2 species are not
    utilized by birds

43
Final thoughts
  • Although the birds in the riparian forest derived
    much of their energy from aquatic insects, about
    2/3 of the diet consisted of terrestrial prey, in
    particular the leaf rollers
  • The greater bird population and therefore greater
    visitation frequency resulted in greater
    predation pressure on leaf rollers in the
    riparian forest
  • Accordingly, the birds thus subsidized can
    depress the population of H. foederatana to
    greater effect in the riparian forest than in the
    upland forest indirect effect of an aquatic
    prey input on a terrestrial herbivore through
    bird predation
  • This study also shows thats aquatic insect
    emergence negatively affects leaf rolling
    Lepidoptera larvae through forest birds

44
Future Research
  • Further examination of the complex food web
    network and the importance of allochthonous prey
    input on the dynamics and structure of
    communities in heterogeneous landscapes

45
References
  • Knight, T. M., McCoy, M. W., Chase, J. M., McCoy,
    K. A., Holt, R. D. (2005). Trophic cascades
    across ecosystems. Nature 473, 880-883.
  • Murakami, M., Nakano, S. (2002) Indirect effect
    of aquatic insect emergence on a terrestrial
    insect population through predation by birds.
    Ecology Letters 5, 333-337

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The END!!!
  • QUESTIONS???
  • I know you have one SHURIN!
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