characterizing tidal inundation of wetlands in the ... · 1/14/2009 · thermal imaging in the...
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Characterizing Tidal Inundation of Wetlandsin the Murderkill Estuary (Kent County, DE)
Thermal Imaging
in the Murderkill Estuary (Kent County, DE)
Tom McKennaDelaware Geological Survey Can temperature
University of Delawarep
be used as an indicator of inundation?
LiDAR
Surface Elevation
TidalInundation
Supported by Kent County & Delaware DNRECJanuary 14, 2009
What causes low DO in the tidal Murderkill River?Issue: low DO (EPA “impaired waters”)
i / h bi h i l i t ti ?
ssue o O ( pa ed ate s )Question: appropriate TMDLs for nutrients? (EPA “pollution control strategy”)
river / marsh biogeochemical interaction?
Webbs Marsh July 3, 2008 low tideWWTP
extensive salt marsh
Waste Water Treatment Plant?NJ
DEBay
DE
Primary Research Question
What processes sources and sinks controlWhat processes, sources, and sinks control low DO in the tidal Murderkill River?
site specific concept al models and
Numerical Water-Quality Modelingsite-specific conceptual models and
input data
parameterizations of processes that
De laware Bay
McGinnis Pondp pare difficult to model explicitly and/or require information not easily obtainable
Andrews La ke
tidal inundation of marshesbiogeochemical cycling in marshesnutrient fluxes in/out marshes
Course y Pond
primary productivitysediment oxygen demand
M cColley Pond
WWTP
Tidal inundation of marshesThe flow of water on salt marsh platforms is still poorly characterized. New conceptual models are being developed
uplandconceptual models are being developed. marsh
platformsecondary
tidal channelChallenges:
i t h
primary tidal
microtopographygroundwater / surface-water interaction anthropogenic alteration (since late 1600s)inundation / vegetation relationship primary tidal
channelinundation / vegetation relationshipvery dynamic systemdense vegetationoverland flow in estuary-scale models
“Discrepancies in tidal phase and elevation in a numerical model can be
overland flow in estuary scale models
p paccommodated by the modeling calibration process but can severely limit the explanatory power and predictive capabilities of the model.” (French, 2003)
Methods for determining inundationHydrodynamic
Model(Overland Flow)
Tide Gages ElevationSurvey
VegetationSurvey
Comment
( )
Model based on distribution of vegetation communities (indirect)
No Few Yes Yes assumes correct
conceptual modelNo No No Yes
Model based on tide and ground-surface elevation (direct)
Yes Many ground-based Yes “Cadillac”
Yes/No Many/Few ground-based or LiDAR
Yes/No
No Few LiDAR No TemperatureNo Few LiDAR No p
Components of common x,y,z datum
“apples to apples” pInundation Studyelevation
marsh surface (LiDAR)very low reliefvery low reliefminimize error and remove bias
instrument locations (e.g. tide level)
preliminary inundation modelhighly parameterized
d t ldata loggerswater level, temperature, and salinity
time-series to document inundation and develop & test modelsair temperature & pressure, solar radiationtemperature on marsh platform (air/water)
Can we use temperature as an indicator of inundation?
thermal imagingCan we use temperature as an indicator of inundation?
Model for tidal inundationPreliminary model makes VERY simple (and wrong) assumption of Instantaneous inundation of entire marsh based on water elevation at Bowers Beach How wrong?Bowers Beach. How wrong?
Working towards more complex representation:
tidal propagation: function for instantaneous tide level for specifiedtidal propagation: function for instantaneous tide level for specified reaches of Murderkill River using data from tide gages at Frederica and Bowers Beach TLr = f(xr,t)
assign TLr to a subset of marshes along the reach
marsh subset inundated based on TLr and set of spatial parameters representing (raster layers):representing (raster layers):
• marsh elevation• attenuation/amplification of tidal amplitude• phase shift of tide based on distance from river/creek/ditch
Testing model of tidal inundationDirect measurement: water level, temperature, and salinity in tidal creeks / ditches using data loggers (time and instrument intensive). Marsh platform
g
g gg ( ) pinstrumentation?
ALTERNATIVE: Can observations of environmental temperature be used to capture spatio temporal dynamics of inundation (lessused to capture spatio-temporal dynamics of inundation (less expensive, more representative of spatial heterogeneity)?
W t fl d h t t fWater flow and heat transfer are highly-coupled processes.
7:19 DST
105
Temperature loggers on marsh platform
Environmental Thermography
Components of common x,y,z datum
“apples to apples” pInundation Studyelevation
marsh surface (LiDAR)very low reliefvery low reliefminimize error and remove bias
instrument locations (e.g. tide level)
preliminary inundation modelhighly parameterized
d t ldata loggerswater level, temperature, and salinity
time-series to document inundation and develop & test modelsair temperature & pressure, solar radiationtemperature on marsh platform (air/water)
Can we use temperature as an indicator of inundation?
thermal imagingCan we use temperature as an indicator of inundation?
Establishing a common vertical datumlow relief on marsh platforms so minimizing elevation error and bias is criticalp g
asset source datum vertical type datum
LiDAR monuments
USGSDELDOT
ellipsoidalellipsoidal
NAD83NAD83monuments
monumentsDELDOT
NGSellipsoidalellipsoidal
NAD83NAD83
monuments NGS orthometric NAVD88tide gages USGS orthometric NGVD29tide gages USGS orthometric NGVD29
tide prediction NOAA tidal MLLW
Geoid model: GEOID03 / VDATUM software (NOAA)convert between ellipsoid, orthometric, and tidal datums
Conducted least squares adjusted GPS-RTK survey8 reference monuments; minimally constrained
Survey correctionsElevation adjustments of up to 55 cm !
Significant for accurate modeling of marsh platform g g pinundation and hydrodynamics in river.
Correction (m)
Locationreference elevation
NGVD29 to
leastsquare
Total(m)Location
value NAVD88squareadjust
(m)
USGS Bowers gage -0.34 -0.24 +0.03 -0.55USGS Webbs gage -0.34 -0.24 +0.03 -0.55USGS Frederica gage 0.00 -0.24 +0.08 -0.16N Bowers ref. monument +0.03 +0.03Barretts Ch. ref. monument +0.08 +0.08LiDAR ref. monument +0.08 +0.08
Components of common x,y,z datum
“apples to apples” pInundation Studyelevation
marsh surface (LiDAR)very low reliefvery low reliefminimize error and remove bias
instrument locations (e.g. tide level)
preliminary inundation modelhighly parameterized
d t ldata loggerswater level, temperature, and salinity
time-series to document inundation and develop & test modelsair temperature & pressure, solar radiationtemperature on marsh platform (air/water)
Can we use temperature as an indicator of inundation?
thermal imagingCan we use temperature as an indicator of inundation?
ELEVATION MAPPINGLIDAR b USGS / NASALIDAR survey by USGS / NASA
Mark Nardi & Wayne Wright
2008; low spring tide; leaf-off
EAARLExperimental
Advanced Airborne Ranging LiDARg g
Digital Elevation ModelDigital Elevation ModelLiDAR survey
scale optimized for
M d kill
scale optimized for marsh topography
Murderkill River
salt marsh
Delaware Bay
uplands
LiDAR data collected for other b i l LiDAR
ypurposes by commercial LiDAR vendors is not optimal for mapping marsh topography.
Components of common x,y,z datum
“apples to apples” pInundation Studyelevation
marsh surface (LiDAR)very low reliefvery low reliefminimize error and remove bias
instrument locations (e.g. tide level)
preliminary inundation modelhighly parameterized
d t ldata loggerswater level, temperature, and salinity
time-series to document inundation and develop & test modelsair temperature & pressure, solar radiationtemperature on marsh platform (air/water)
Can we use temperature as an indicator of inundation?
thermal imagingCan we use temperature as an indicator of inundation?
Cumulative Probability of Tide Being Below an n
Tide Being Below an Absolute Elevation
n el
evat
ion
MTL
MLL
WM
LW
85% of time b l MHW
Bowers
elow
giv
en
75th %
HH
W
HW
below MHW3 gages (USGS)
FredericaWebbs Slough
tidal datums shown for Bowers ter l
evel
be
medianMHMH
45% of time below MTLtidal datums shown for Bowers
(VDatum)
of ti
me
wat
25th %
% fPreliminary model makes VERY
simple (and wrong) assumption of Instantaneous inundation based on
t l ti t B B h Elevation (m)-1.5Frac
tion
o 2% of time below MLW
water elevation at Bowers BeachBut how wrong?
Elevation (m)
Digital Elevation ModelLiDAR
Delaware Bay
Murderkill RiverRiver
uplands
salt marsh
uplands
salt marsh
elevation < mean tide level0 02 m NAVD88-0.02 m NAVD88LSA
using tide levels from Bowers Beach gage
elevation < 0.4 m0 4 m NAVD880.4 m NAVD88LSA
using tide levels from Bowers Beach gage
elevation < mean high water0 6 m NAVD880.6 m NAVD88LSA
using tide levels from Bowers Beach gage
elevation < mean highest high water 0 75 m NAVD880.75 m NAVD88LSA
using tide levels from Bowers Beach gage
elevation < 0.9 m 0 9 m NAVD88 (> MHHW)0.9 m NAVD88LSA (> MHHW)
using tide levels from Bowers Beach gage
Components of common x,y,z datum
“apples to apples” pInundation Studyelevation
marsh surface (LiDAR)very low reliefvery low reliefminimize error and remove bias
instrument locations (e.g. tide level)
preliminary inundation modelhighly parameterized
d t ldata loggerswater level, temperature, and salinity
time-series to document inundation and develop & test modelsair temperature & pressure, solar radiationtemperature on marsh platform (air/water)
Can we use temperature as an indicator of inundation?
thermal imagingCan we use temperature as an indicator of inundation?
Data Loggers in Webbs Marsh~ 1 year at 6-minute sampling interval
Murderkill R
temperature, salinity, leveltemperature
temperature, salinity, level, velocity, pH, DO R.
23
1Murder-
kill R
WSR
Likely Temperature Signals from Inundation?
season temperature
air water
day nitespring warm cool warm/coolsummer warm cool warmfall cool cool warm/coolwinter cool cold coolwinter cool cold cool
Temperature signals of inundation at 3 sites on the marsh platform (over 7 days) inundation progresses through time from site 1 to site 3
Jun 1, 2008 Jun 8, 2008daynight start of
1daynight
oCstart of
inundationat site 1
start of inundation
at site 3
2oC
3oC
air temp.Water temperature @ Webbs Slough (WS)
oC
Webbs Slough (WS) tide
p
temperature difference (site 1 – site WS)
Webbs Slough (WS) tidem
Phase lag of inundation relative to tide level at Webbs Slough
area minutes
• secondary ditches 10-20• Spartina alterniflora 20-40
near ditches• Spartina alterniflora 60-90
away from ditches • Spartina patens 60-90p p
Components of common x,y,z datum
“apples to apples” pInundation Studyelevation
marsh surface (LiDAR)very low reliefvery low reliefminimize error and remove bias
instrument locations (e.g. tide level)
preliminary inundation modelhighly parameterized
d t ldata loggerswater level, temperature, and salinity
time-series to document inundation and develop & test modelsair temperature & pressure, solar radiationtemperature on marsh platform (air/water)
Can we use temperature as an indicator of inundation?
thermal imagingCan we use temperature as an indicator of inundation?
MULTI-SPECTRAL IMAGING
Reflected Energy Emitted EnergyThermal Bands
SWIR MWIR LWIRNIRUV Visible
1.7µm 3.0µm 5.0µm 14.0µm8.0µm1.0µm0.4µm
thi t dthis study
Environmental Thermography(Thermal Imaging of the Environment)
• measure “apparent” temperature of remote surfaces located centimeters to kilometers away
• absolute temperature can be calculated emissivity of a material (e.g. water, sediment, vegetation) y ( g , , g )geometry of the observing system
• can be usedcan be used as a quick investigative tool for detailed lab / field studies of dynamic processes
• natural engineered industrial• natural, engineered, industrial
Imagingg gPlatforms
Temperature Time Series of Tidal Mixing in Webbs Slough (May 15, 2008) 12 18°C
lift platform visual
5:49 DST 6:04 DST 6:19 DST5:34 DST
Cooler water from the Murderkill River flows into Webbs Slough during flood tide and back out during ebb tide
flood
6:34 DST
15 30 45
7:04 DST 7:19 DST
sunrise0 minflood tide
6:49 DST
60 90 10575
high tide
ebbtide60
7:34 DST 8:04 DST 8:19 DST7:49 DST
90 10575 tide
120 150 165 min135
Temperature Time Series Showing Inundation of Marsh Platform
visual8:44 PM ESTflood tidewarmer water (gray blue) oncolder (red)
marsh surface
12/13/2008BB
Amarsh surface
thermal imager location816-817A
9:04 PM ESThigh tideB
882-885A
9:42 PMebb tideB
July 31, 2008early evening
1062-1064A
Image of Marsh Platform Inundationwarmer water flowing onto
Webbs MarshDecember 13, 2008
high spring tide ld i ( bf i )
gcold marsh surface cold morning (subfreezing)
helicopter platform
inundated platform
is “warm” (orange)
A
AB
(orange)
AB
channels are “hot” (yellow)
Thermal ImageDifferentiating
Sources
cold water (black) ponded on marsh
Thermal ImageSources of Water
cold water (black) ponded on marsh platform after recent rain event
Visual Image
BB
A
B
A
warm water (white) in Brockonbridge Gut Webbs Slough and ditches
12/13/2008 9:56 AM high tide
Gut, Webbs Slough, and ditches
ConclusionsConclusions
S lt h l ti i M d kill E tSalt-marsh elevations in upper Murderkill Estuary (Frederica) are lower than lower estuary (Bowers Beach)
Common vertical datum is critical for quantifying tidal inundation using in-situ instrumentation.
Environmental temperature can be used to capture spatio-temporal dynamics of inundation.– inexpensive in-situ data loggersinexpensive in situ data loggers– environmental thermography