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Reciprocal subsidies: Dynamic interdependence between terrestrial and aquatic food webs

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Title: Reciprocal subsidies: Dynamic interdependence between terrestrial and aquatic food webs


1
Reciprocal subsidies Dynamic interdependence
between terrestrial and aquatic food webs
  • Shigeru Nakano and Masashi Murakami

2
Why study reciprocal trophic exchange?
  • Across-habitat transfer of energy can shape
    communities
  • Energy flows from high to low
  • However, 2-way flow based on seasonality has not
    been studied
  • (Polis, Anderson, Holt 1997 Cloc Garman
    1995)

3
The facts
  • Energy of stream and forest tightly coupled to
    temperature and light
  • Strong edge effects create energetic interaction
    between the two zones
  • Terrestrial plant productivity peaks in summer
    and decreases as temperature drops in fall
  • Stream productivity highest when trees defoliate,
    and decreases as trees block light in summer
  • Hypothesis This difference in peaks creates
    reciprocal energy exchange at different times of
    year

4
Study Site
  • 10 Ha plot along Horonai Stream in Tomakomai
    Experimental Forest, Hokkaido, Japan
  • Riparian zone dominated by Ash, Cherry, Oak
  • 2-5m stream 97 shaded in summer
  • 14Km long, gradient lt1
  • Air temp between -15 and 25C
  • Water temp always 6C

5
The Consumers
  • Birds 4 all-year residents, 5 summer
    (May-August) residents, 1 winter (Oct-March)
    resident
  • Fish 4 water column fish (2 Oncorhynchus spp., 2
    Salvelinus spp.) and 1 benthic fish (Cottus)

6
Methods Prey abundance and flux
  • Terrestrial
  • Abundance determined by leaf beating and
    catching falling bugs in 80x80 cm tray once a
    month from 8o trees
  • Flux measured from catches in 15 pan traps (1x1 m
    x 15cm deep) held in stream current (traps set
    for a week once each month)
  • Biomass dried and weighed

7
Methods Prey abundance and flux
  • Aquatic
  • Abundance determined via 225-µm mesh Surber net
    sampler (25x25 cm, 1 m deep) from 12 locations
    once a month
  • Flux measured from numbers in emergent traps
    (1x1X1m, .5mm mesh) placed in 18 locations, 4
    days twice a month
  • Biomass dried and weighed

8
Methods Consumer diet
  • Birds examined in 20m² areas for 5 hours
    immediately after dawn every day.
  • Any bird entering an area was followed for as
    long as possible within 40m of the area.
  • Assessments were made for 53.6 of prey caught,
    and classified into terrestrial or aquatic
  • Bird abundance then determined by mapping method

9
Methods Consumer diet
  • Fish caught for 5 hours after dawn every day
    using a backpack electro-fishing unit
  • Stomachs were pumped and fish were returned to
    stream. Contents preserved and classified in lab.
  • Fish abundance then determined by three-pass
    removal method in four areas (50m long, 3.5m wide)

10
Results
  • Terrestrial biomass greatest in leafing period
    (June-August), and terrestrial flux into stream
    proportional to biomass
  • Terrestrial flux comprised 60-100 of aquatic
    energy budget during leafing period (except in
    Cottus)

11
Results
  • Aquatic biomass was highest in spring, just
    before leafing began. Aquatic flux onto land was
    not correlated with biomass, but did peak at
    approximately the same time.
  • Aquatic flux accounted for 50-90 of bird energy
    budget during the defoliation period.

12
Significance?
  • The authors indeed found a seasonal asynchrony in
    prey flux
  • Such differences greatly augment the energy
    supply of linked habitats
  • Therefore, this has serious consequences on
    habitat loss that may not have been previously
    considered.

13
Good luck on your finals!
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