Andrew Schroth Fundamental Lake Process Research Question - - PowerPoint PPT Presentation

andrew schroth fundamental lake process research question
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Andrew Schroth Fundamental Lake Process Research Question - - PowerPoint PPT Presentation

Lake Processes Group Update R esearch on A daptation to C limate C hange Andrew Schroth Fundamental Lake Process Research Question (Formerly Q1) What is the relative importance of endogenous (in- lake) processes versus exogenous (to-lake)


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SLIDE 1

Lake Processes Group Update Research on Adaptation to Climate Change

Andrew Schroth

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SLIDE 2

Fundamental Lake Process Research Question (Formerly Q1)

External Internal

  • What is the relative importance of endogenous (in-

lake) processes versus exogenous (to-lake) processes to eutrophication and harmful algal blooms in Lake Champlain?

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SLIDE 3

Approach to Question 1

  • What are the important sources of

nutrients & sediment to the lake?

  • How do land use and climate affect the

nature and strength of these sources?

  • How are nutrients and sediments

transformed and cycled within the lake?

  • How do the loadings of these materials

and hydrodynamics affect lake processes and ecosystems?

Sediment Release Accumulation ICE Nutrients Oxygen Oxygen Wind

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SLIDE 4

Presentation Structure

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SLIDE 5

Missisquoi Winooski

Agriculture: runoff, groundwater, soils, stream bank erosion Forested: soils, groundwater, roads, channel migration, erosion Urban: stormwater runoff, wastewater, stream erosion

Focus Watersheds

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SLIDE 6

P Distribution: Agricultural Field (corn/hay) through riparian zones/stream bank

What we have accomplished?

Source area characteristics: Soil Chemistry

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SLIDE 7

Hazard Road Hay Field Wood’s Hill Road Hay Field

Total Phosphorus Degree of Phosphorus Saturation

VT avg VT avg

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SLIDE 8

216 soil samples from Missisquoi corn field transects. Median =950 mg/kg 54 surface soil samples from Missisquoi corn fields transects. Median =1122 mg/kg

Total phosphorus in Vermont stream corridor soils

c d

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SLIDE 9

What we have accomplished?

Instrumented key sub-watersheds

North Troy (MS) East Berkshire (MS) Hungerford Brook Swanton (MS) RACC

Missisquoi Winooski

Essex Jnct (MS)

  • W. Branch, Little R.

Ranch Brook Mad R., Moretown Montpelier (MS)

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SLIDE 10

Capture Storm Event Biogeochemical Evolution with Automated Sampling

ISCO Programs Target Storms

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SLIDE 11

Watershed and Lake Sampling What we have accomplished?

Integrated water sampling & analysis network

Johnson State College Undergraduate and graduate students have been directly involved in installation, maintenance, sampling, analysis, and data management.

  • St. Michael’s

College

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SLIDE 12

Ice Ice breakup Snow gone from fields April 15th Rainstorm Active snowmelt period

High-Frequency Targeted Snowmelt Sampling

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SLIDE 13

NEWRnet Sensor Network: Schroth,

Bowden, Vaughan, Jerram (UVM), Shanley (USGS), Vermilyea (Castleton)

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SLIDE 14

Research Questions

  • Can we detect and describe regional

hot moments? Examples: late summer storms, snowmelt, rain on snow, autumn leaf fall, large regional storms or droughts

  • How does local watershed water

quality respond to extreme events across variable landcover?

  • Anthropogenic hot moments in

agricultural systems? BMP effects?

Harms and Grimm, 2008

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SLIDE 15

Met Station

0.5 m 2 m 3 m 0.15 m 1 m 2 m 2.5 m 3 m

Weekly Depth Grabs Vertical Profiler

ISCO

UVM Biogeochemical Station Middlebury Hydrodynamics

What we have accomplished?

Missisquoi Bay Advanced Environmental Monitoring Sensor Array

  • Water depth ~ 3-4 m
  • SE portion of bay insulated

from S, E, W winds

  • Site of the most intense BGA

blooms

  • 2012-present continuous

data (Spring-Fall)

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SLIDE 16

UVM Biogeochemical Sampling Strategy

  • Hourly:

 Sonde measurements (DO, pH, turbidity, temp, phycocyanin, chlorophyll a) (5 depths)  Weather, river variables (temp, wind, discharge, water level)

Every 8 hours (5am, 1pm, 9pm)

 Total nitrogen, total phosphorus, total metals (3 depths)

  • Weekly

 SRP, TDP, NO3

  • , NH4

+, dissolved metals, colloidal metals,

phytoplankton, zooplankton, TSS, sediment cores (biweekly)

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SLIDE 17

150 200 250 300 20 40 60 80

julian date BGA 2012 2013 2014

150 200 250 300 5000 15000

julian date Discharge

150 200 250 300 10 15 20 25 30

Temp C

Ongoing Bloom Stage Monitoring

High temporal resolution data reveal drivers of resource limitation and cyanobacterial blooms during a dry summer (Isles et al. to be submitted to L&O)

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SLIDE 18

What are we working on?

Bioindicators to explore the effects of nutrient dynamics on aquatic food web structure

Sampling & identification Phytoplankton Zooplankton Benthic invertebrates Aquatic plants Fish FlowCAM in 2013

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Light Limitation and Alternate Stable States: Isles

3 6 9 12 15 18 21

  • 2.0
  • 1.5
  • 1.0
  • 0.5

Growth Phase

3 6 9 12 15 18 21

  • 2.0
  • 1.5
  • 1.0
  • 0.5

Peak Bloom

3 6 9 12 15 18 21

  • 2.0
  • 1.5
  • 1.0
  • 0.5

Late Bloom

Hour MRD

Competition for light and the role of buoyancy regulation in stabilizing alternate stable states ASLO conference 2014

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SLIDE 20
  • Cyanobacteria produce very low levels of

essential fatty acids(EFA)

  • Decreases zooplankton EFAs, growth, and

fecundity

  • Decrease available essential fatty acids to

fish and could have impacts on their fitness

Consequences of Cyanobacteria on Essential Fatty Acid Limitation in Fish (Gearhart and Stockwell)

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SLIDE 21

Yellow Perch

  • Preliminary results show trends

similar to our hypothesis

  • Further analysis of liver tissue

will show complete picture

  • Lab experiments are in

progress to determine the exact impacts of BGA on perch fatty acids

Fish Studies: Preliminary Results (Gearhart and Stockwell)

DO CYANOBACTERIA BLOOMS SHIFT FOOD-WEB PATHWAYS IN FRESHWATER LAKES? Gearhart ASLO 2014

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SLIDE 22

2014/2015 Hydrodynamic Array (Presently Operational, T. Manley)

Vertical Temp. Strings ADCPs Water Level

  • Atm. Pressure

Manley, 2014

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SLIDE 23

Perzan & Manley, 2014

Bottom 1m

Average of 4 bins with 2-Hr Filter

Top 1m

Average of 4 bins with 2-Hr Filter

High Spring River Inflow Drives Consistent Mean CCW Circulation

What we have accomplished?

Dynamic circulation models

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SLIDE 24

2013

Fishbin & Manley, 2014

2013 & 2014

What we have accomplished?

High-Resolution Bathymetric Mapping

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SLIDE 25

What we have accomplished?

Spatial Sampling of Sediment: Sediment Trend Analysis and Benthic Community Mapping P Manley, D. McCabe Sampling Conducted 2013, Analyzed 2014

Clay% Silt% Sand %

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SLIDE 26
  • Transport lines

group into 4 Transport Environments (TE)

  • Each TE has

transport related to each other

Sediment Transport Modeling

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Microfaunal Sediment Study– Preliminary Trends in Species Location

  • Distribution and abundance
  • f D. polymorpha (Zebra

mussels) in Missisquoi Bay

  • D. polymorpha most abundant
  • n east side of bay, absent in

SE corner

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SLIDE 28

What we have accomplished?

Drivers of P and Metals Dynamics in Missisquoi Bay: Novel Holistic Approach (Giles)

Used physical and biogeochemical high-frequency sensor data to identify periods of: Stability and Disturbance

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SLIDE 29

Water Column: Stable: Enriched Bottom Water Mn, Pronounced DO Stratification Disturbed: Minimal Stratification, low Mn, SRP/Fe depend on degree riverine input

Drivers of P and Metals Dynamics in Missisquoi Bay:

Novel Holistic Approach (Giles)

Sediment: Stable: Depletion of P, Fe, Mn from sediment Disturbed: Accumulation of P, Fe, Mn in sediment Tight P Cycling in M. Bay!

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Conceptual Model: Stable vs. Disturbed

Water Column Depth Sediment Depth [Reac ve P, metals] [SRP, metals]

T DO Reduc ve dissolu on

  • f

metals in surface sediments leads to P and metals diffusion into bo om waters. Warm, calm condi ons lead to thermal stra fica on, water column stability and DO deple on in bo om waters..

hv BGA, Chl A

STABLE

Water Column Depth Sediment Depth [Reac ve P, metals]

T DO P and metals from

  • verlying

water and lower sediment layers are re-oxidized and accumulate in surface sediments .

Wind mixing, river inflows BGA dispersed

MIXED

Water column mixing disrupts thermal stra fica on and stability and

  • xygenates
  • bo om

waters.

  • Air

Wate Interf Sedim Wate Interf Oxidized layer [SRP, metals]

PHOSPHORUS AND METALS MOBILITY IN THE SEDIMENT-WATER CONTINUUM

  • OF

A SHALLOW, FRESHWATER LAKE UNDER STRATIFIED AND MIXED WATER-COLUMN CONDITIONS

ACCUMULATION DEPLETION

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Welcome DongJoo (DJ) Joung!

What are we working on? Spatial SWI Dynamics

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SLIDE 32

Missisquoi Bay

What We have Accomplished?

Under Ice Biogeochemical/Hydro Dynamics

Rain on Snow Deep Cold (1 m of ice) Spring Thaw

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Water Column: Ice Development(Stable): Enriched Bottom Water Mn, SRP, Pronounced DO Stratification Rain on Snow/Thaw (Disturbed):Inverted stratification of SRP, Fe low Mn, DO Stratification minimal

Under Ice Metal/P Dynamics

Water Column: Ice Development(Stable): Enriched Bottom Water Mn, SRP, Pronounced DO Stratification Rain on Snow/Thaw (Disturbed):Inverted stratification of SRP, Fe low Mn, DO Stratification minimal Sediment: Continuous release of P, Fe, Mn during prolonged cold, but re- accumulation during thaw

  • r rain on snow

Tight cycling of P during winter

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SLIDE 34

Bathymetry River Inputs, Main lake level Initial water levels, temp Wind (speed, direction) Temp RH Pressure Solar Radiation Cloud Cover Initial nutrients, phytoplankton, zooplankton Phyto growth and nutrient uptake parameters Initial mussel densities Initial sediment nutrient concentrations, bulk density, sediment diagenesis parameters

Advanced Aquatic Ecosystem Model (A2EM)

  • 240m grid cells
  • 5 vertical layers
  • > 30 state variables simulated
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A2EM Progress

  • EFDC calibrated for 2012, 2013
  • RCA input data and boundary conditions

prepared, ready for parameter calibration

Aug Sep Oct 10 15 20 25 30

Modeled v. Observed Temperature, Surface, Main Site 2012

  • Deg. C

Observed Calib_010 Aug Sep Oct 10 15 20 25

Modeled v. Observed Temperature, ~2m, Main Site 2012

  • Deg. C

Observed Calib_010 Jun Jul Aug Sep Oct 10 15 20 25 30 35

Modeled v. Observed Water Temp, Surface, 2013

buoyDataHourly$temp0.5m Observed Modeled Jun Jul Aug Sep Oct 10 15 20 25 30 35

Modeled v. Observed Water Temp, 2m, 2013

buoyDataHourly$temp2m Observed Modeled

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SLIDE 36

Carlson R. E. 1977. Limnology and Oceanography. 22: 361-369 Xu Y., Schroth A., Rizzo D. 2014. Limnology and Oceanography: Methods (Submitted)

Eutrophication assessment (Trophic State Index , TSI): Original framework (Carlson, 1977): States of Lake Champlain: Cluster α: Eutrophic with high risks of phosphorus; Cluster β: oligotrophic and mesotrophic without risks of phosphorus 21st century framework: Integrating statistical advance (i.e. Upper bound method) and increasingly availability of lake- specific datasets (e. g. Lake Champlain)

Statistical Modeling of Lake Datasets

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Big Data – Q1

  • Variety

– Fundamentally diverse, variable temporal and spatial

  • ffset, complicates database design for lake

– Aquarius

  • Velocity

– Variable Frequency (collection and retrieval)

  • Veracity

– Initial conditions and calibrate models – QA/QC by responsible research group