Organic matter dynamics in the Kuparuk River Influence of Temperature and Light on Rates of Inorgani - PowerPoint PPT Presentation

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Organic matter dynamics in the Kuparuk River Influence of Temperature and Light on Rates of Inorgani

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... and Light on Rates of Inorganic Nitrogen Transport by Algae in an Arctic Lake ... Arctic grayling (Thymallus arcticus) only fish present in Kuparuk; about 75 ... – PowerPoint PPT presentation

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Title: Organic matter dynamics in the Kuparuk River Influence of Temperature and Light on Rates of Inorgani


1
Organic matter dynamics in the Kuparuk
RiverInfluence of Temperature and Light on
Rates of Inorganic Nitrogen Transport by Algae in
an Arctic Lake
2
  • Since the late 1970s, research has been conducted
    on the upper 24.6 km of the river, from its
    headwaters in the foothills of the Brooks Range
    to its intersection with the pipeline and Dalton
    highway. Minimal terrestrial plant cover,
    streamside patches of dwarf birches and willows,
    often less than 1 m.
  • Entire watershed is underlain with permafrost,
    greatly reduces seepage. Thaw depth beneath
    riverbed has not been thoroughly investigated.
  • Frozen solid from Sept-May, Air temp winter -30
    to -40, summer 10 to 18
  • Mean annual water 1.7C, open water period 9C
  • Average annual precip 18cm

3
Inputs
  • Stream rocks with intact epilithic communities
    placed in closed, artificially-lighted chambers,
    measure dissolved oxygen concentration as index
    of primary production
  • Over the 5-year study, GPP averaged 22.5
    mg/(m²h)
  • 3-month growth season, production occurs 24
    hours/day and not at all during the rest of the
    year, yielding an average of 49 g/(m²y)
  • Net primary prod., by subtracting epilithic
    respiration from GPP, 11.4 mg/(m²h), or 25
    g/(m²y)
  • Bryophyte moss GPP 55 g/(m²y) NPP 39
    g/(m²y), however, production may be
    overestimated due to fertilizer runoff.
    Allocthonous litter was almost exclusively peat
    and tundra plant fragments. Meandering path
    erodes streambanks, the major source of
    particulate organic matter
  • Hyporheic rock communities GPP 5 g/(m²y), NPP
    1 g/(m²y)
  • DOM and POM values are not available

4
Outputs
  • Respiration of epilithic algae measured in
    darkened chambers
  • Averages 24 g/(m²y) Bryophyte moss 16 g/(m²y)
  • Respiration 24 hours/day during growth, near
    zero rest of year
  • Respiration may also be overestimated due to
    fertilization of land
  • No data for heterotrophic respiration
  • Exports of DOM, POM, and CPOM gt300 µm, complicated

5
Standing crops
  • Four categories of BOM UFBOM, FBOM, LBOM, and
    VLBOM
  • FBOM and UFBOM cylinder placed on stream bottom,
    rocks inside scrubbed, gravel stirred up to
    resuspend organic matter
  • LBOM filtered with 300 µm mesh
  • VLBOM hand-collected, mostly peat and woody
    debris
  • Algal standing crop on stream bottom convert
    total chlorophyll content into carbon units using
    a 501 CChl weight ratio 1.1 g/m²
  • Bryophyte biomass estimate percentage of stream
    bottom covered select plots, remove, dry, and
    weigh plot against estimated cover total
    estimated bryophyte biomass 20 g/m²
  • Benthic invertebrates primarily insects mean
    summer 1.3 g/m²
  • Arctic grayling (Thymallus arcticus) only fish
    present in Kuparuk about 75 adults/km, 2
    young/m², total standing crop 0.2 g/m²

6
Chlorophyll and Bryophtye
7
Insects
(Cadisfly)
8
Fish
9
Conclusions 1
  • Dominant source of organic matter is allocthonous
    DOM
  • Wet, cold soil rich in biomass, underlain by
    permafrost
  • 2nd largest peaty soil organic matter, eroded
    from stream banks
  • judged to be of low quality due to slow decay
    rate
  • Native primary production contributes much less
    organic matter
  • higher quality material for bacteria and
    consumers
  • Bryophyte production may equal epilithic algal
    production
  • Important moss tissues are not as easily
    decomposed as diatoms and algae
  • Key unknowns in organic matter budget rates of
    biological mineralization of allocthonous DOM and
    POM.
  • Especially how it affects higher trophic levels,
    such as insects and fish

10
Effects of Light and Temeprature
  • Concentrations during ice-free June-Sept in
    µmol/L
  • Nitrate 0.10 Ammonium 0.15 total dissolved
    Phosphorous 0.15
  • Soluble reactive Phosphorous lt0.03
    (undetectable)
  • Thermal stratification July-August, surface water
    15C
  • Kinetic experiments indicate uptake is limited by
    external DIN concentration
  • 24 hour bioassay experiments show that
    N-enrichment stimulates photosynthesis as often
    as P-enrichment

11
Inlet mixing
12
Injection of traceable dye Rhodamine
13
Toolik Lake bathymetric map
14
Weather Summary
15
Temperature Dependence Experiments
  • Ambient water temp range 8-14C
  • Data pooled, no significant relation found
    between increasing values of Topt and increasing
    values of Tamb
  • DIN transport rates at Tamb were temp. limited
  • NH4 transport rate far exceeded that of NO3- in
    every experiment

Optimal temp range for NO3- and NH4 16-22C,
19-23C
16
Ratio of transport rates
  • Values of ratio ranged from 1.8 to 5.8, but
    remained generally constant at 2-3 in all
    experiments until temp became supraoptimal.
  • At that point, relative transport rates of
    NO3-declined more dramatically than those of
    NH4, leading to the sharp increase in ratio

17
Light Dependence Experiments
  • Typical response curves show that at all levels
    of irradiance, rates of NH4 transport were
    always greater than corresponding rates of NO3-.
  • Suggested by MacIsaac and Dugdale that dark DIN
    transport is not necessarily a constant
    proportion of light transport, but rather a
    distinct process that occurs in the dark or under
    low light.
  • Ignore dark DIN transport and fit
    Michaelis-Menten relationship to light
  • Rate Ratedark Ratemax (I/(KLT I))

18
Light Dependence Experiments
  • Depressed transport was noted in clear bottles in
    experiments LT3 and LT4 perhaps photoinhibition,
    eliminated from curve so as not to affect
    calculations of Ratemax and KLT

19
Chlorophyll-specific NO3- transport profile for
Toolik Lake
  • Ambient NO3- levels were so low throughout that
    limitation of NO3- rate/Chl was probably never
    achieved solely by light.
  • Decreased chlorophyll-specific transport rate
    with depth must be interpreted in terms of the
    combined stress of NO3- limitation and
    sub-optimal light.
  • Conclude ambient concentration of DIN is most
    important, light plays secondary role in
    regulating DIN transport by phytoplankton

20
Conclusions 2
  • Maximum rates of DIN transport in algae are
    light-dependent from marine and temperate lake
    systems to a high-latitude lake where light is
    continuous throughout the growing season.
  • NH4 is the preferred inorganic nitrogen source
    for algal nutrition to include arctic freshwater
    phytoplankton as well.
  • First to document the influence of temperature on
    nitrogen-saturated rates of DIN transport in
    natural plankton population
  • Results can be used to predict phytoplankton
    response to unplanned disturbances through
    nutrient addition to arctic lakes, especially as
    public access to the Alaskan arctic increases
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