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CHAPTER 12:CHAPTER 12:Remote Sensing ofRemote Sensing of
WaterWaterWaterWaterREFERENCE: Remote Sensing REFERENCE: Remote Sensing of the Environment of the Environment John R. Jensen (2007)John R. Jensen (2007)Second EditionSecond EditionPearson Prentice HallPearson Prentice Hall
Why we study Why we study y yy ythe waterthe water
with remote with remote sensing?sensing?
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THE BLUE PLANETTHE BLUE PLANET74% of the Earth’s surface is water
WATER RESERVOIRSWATER RESERVOIRS
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PROCESSES PROCESSES AFECTING THE AFECTING THE
REMOTE REMOTE SIGNALSIGNAL
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DIFFERENT LAYERSDIFFERENT LAYERS
Total radiance, (Lt) recorded by a remote sensing system over water is a function of the electromagnetic energythe electromagnetic energy received from:
Lp = atmospheric pathradiance
Ls = free-surface layer reflectancereflectance
Lv = subsurface volumetric reflectance
Lb = bottom reflectance
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The total radiance, (Lt) recorded by a remote sensing system over a waterbody is a function of the electromagnetic energy from four sources:
Lt = Lp + Ls + Lv + Lb
L i h h di d d b l i f h d lli l ( ) d
Water Surface, Subsurface Volumetric, and Bottom Radiance
• Lp is the the radiance recorded by a sensor resulting from the downwelling solar (Esun) and sky (Esky) radiation. This is unwanted path radiance that never reaches the water.
• Ls is the radiance that reaches the air-water interface (free-surface layer or boundary layer) but only penetrates it a millimeter or so and is then reflected from the water surface. This reflected energy contains spectral information about the near-surface characteristics of the water.
L i th di th t t t th i t i t f i t t ith th i /i i• Lv is the radiance that penetrates the air-water interface, interacts with the organic/inorganic constituents in the water, and then exits the water column without encountering the bottom. It is called subsurface volumetric radiance and provides information about the internal bulk characteristics of the water column.
• Lb is the radiance that reaches the bottom of the waterbody, is reflected from it and propagates back through the water column, and then exits the water column. This radiance is of value if we want information about the bottom (e.g., depth, color).
BRIGHTNESSBRIGHTNESSIS CHANGEDIS CHANGEDTO TO LLt t AND AND RRrsrs
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WATER SURFACE CONDITIONSWATER SURFACE CONDITIONSTHAT AFFECT THAT AFFECT LLSS
Examples of Absorption of Near-Infrared Radiant Flux by Water and Sunglint
Black and white infrared photograph of water
bodies in Florida
Black and white infrared photograph with
sunglint
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CHANGESCHANGESIN DEPTHIN DEPTHAFFECTAFFECTAFFECTAFFECT
LLS S AND AND LLVV
BATHYMETRYBATHYMETRY
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Th b t l th i f di i i ti
Monitoring the Surface Extent of Water Bodies
The best wavelength region for discriminatingland from pure water is in the near-infrared andmiddle-infrared from740 - 2,500 nm.
In the near- and middle-infrared regions, waterbodies appear very dark even black becausebodies appear very dark, even black, becausethey absorb almost all of the incident radiantflux, especially when the water is deep and pureand contains little suspended sediment ororganic matter.
Water Penetration
Cozumel IslandCozumel Island
SPOT Band 1 (0.5 - 0.59 mm) green
SPOT Band 2 (0.61 - 0.68 mm) red
SPOT Band 3 (0.79 - 0.89 mm) NIR
PalancarPalancar ReefReef Caribbean SeaCaribbean Sea
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What we Measure
SEPARATING THE SEPARATING THE REMOTE SIGNALREMOTE SIGNAL
Water Column Reflected RadianceWater Column Reflected Radiance
Reflected Bottom RadianceReflected Bottom Radiance
FromNEMO OverviewNemo.nrl.navy.gov
• Inherent Optical Properties• Bottom Reflectance (Albedo)
PROPERTIES PROPERTIES PROPERTIES PROPERTIES AFFECTING THE AFFECTING THE WATER LEAVING WATER LEAVING RADIANCE (LRADIANCE (L ))RADIANCE (LRADIANCE (LWW))
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When conducting water-quality studies using remotely sensed data we are
Spectral Response of Water as a Function of Organic and Inorganic Constituents - Monitoring Suspended Minerals (Turbidity), Chlorophyll, and Dissolved Organic Matter
When conducting water-quality studies using remotely sensed data, we areusually most interested in measuring the subsurface volumetric radiance, Lvexiting the water column toward the sensor. The characteristics of this radiantenergy are a function of the concentration of pure water (w), inorganic suspendedminerals (SM), organic chlorophyll a (Chl), dissolved organic material (DOM),and the total amount of absorption and scattering attenuation that takes place inthe water column due to each of these constituents, c(λ):
Lv = f [Wc(λ), SMc(λ), Chlc(λ), DOMc(λ) ]
It is useful to look at the effect that each of these constituents has on the spectralreflectance characteristics of a water column.
Absorptionin
Pure Water
Molecular water absorption dominates in the ultraviolet (<400 nm) and in the yellow through the near-infrared portion of the spectrum (>580 nm). Almost all of the incident near-infrared and middle-infrared (740 -middle-infrared (740 -2500 nm) radiant flux entering a pure water body is absorbed with negligible scattering taking place.
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Scatteringin
Pure Water
S i i hScattering in the water column is important in the violet, dark blue, and light blue portions of the spectrum (400 - 500 nm). This is the reason water appears blue to our eyes. The graph truncates theThe graph truncates the absorption data in the ultraviolet and in the yellow through near-infrared regions because the attenuation is so great.
Minerals such as silicon, aluminum, and iron oxides are found in
Spectral Response of Water as a Function of Inorganic Constituents
suspension in most natural water bodies.The particles range from fine clay particles ( 3 - 4 μm indiameter), to silt (5 - 40 μm), to fine-grain sand (41 - 130 μm),and coarse grain sand (131 - 1250 μm).Sediment comes from a variety of sources including agricultureerosion, weathering of mountainous terrain, shore erosioncaused by waves or boat traffic and volcanic eruptions (ash)caused by waves or boat traffic, and volcanic eruptions (ash).Most suspended mineral sediment is concentrated in the inlandand nearshore water bodies.Clear, deep ocean far from shore rarely contains suspendedminerals greater than 1 μm in diameter.
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AMOUNT OF TURBIDITYAMOUNT OF TURBIDITY
In situ Spectroradiometer Measurement of Clear
Water with Various Levels of Clayey and Silty Soil
Suspended Sediment
clay
1 5
2
2.5
3
3.5
4
4.5
5
Per
cent
Ref
lect
ance
50
100
150 200
250
clear water
300
1,000 mg/l
Clayey soil
Suspended Sediment Concentrations
silt
400 450 500 55 0 600 65 0 700 75 0 800 85 0 9000
0.5
1
1.5
Wavelength (nm)
clear water
8
10
12
14
ctan
ce
1,000 mg/l
600
150
200 250 300 350 400
450 500 550
a.
Silty soil Reflectance peak shifts toward longer wavelengths as more suspended sediment is added
Lodhi et al., 1997; Jensen, 2000400 450 500 55 0 600 65 0 700 75 0 800 85 0 900
0
Wavelength (nm)
2
4
6
8
Per
cent
Ref
lec
clear water
50
100
b.
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Space Shuttle Photograph of the Suspended
Sediment Plume at the M th f thMouth of the
Mississippi River near New Orleans,
Louisiana
Mississippi River Plume-TM
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Mayaguez Bay-AOCI
Añasco River Plume-ATLAS
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Añasco River Plume-IKONOS
Culebrinas River Plume-IKONOS
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Plankton is the generic term used to describe all the living organisms (plant andanimal) present in a waterbody that cannot resist the current (unlike fish).
Spectral Response of Water as a Function Spectral Response of Water as a Function of Organic Constituents of Organic Constituents -- PlanktonPlankton
animal) present in a waterbody that cannot resist the current (unlike fish).Plankton may be subdivided further into algal plant organisms (phytoplankton),animal organisms (zoolankton), bacteria (bacterio-plankton), and lower plantforms such as algal fungi.Phytoplankton are small single-celled plants smaller than the size of a pinhead.Phytoplankton, like plants on land, are composed of substances that containcarbon.Phytoplankton sink to the ocean or water-body floor when they die. All
h l k i b di i h h h i ll i iphytoplankton in water bodies contain the photosynthetically active pigmentchlorpohyll a.There are two other phytoplankton photosynthesizing agents: carotenoids andphycobilins.Bukata et al (1995) suggest, however, that chlorphyll a is a reasonablesurrogate for the organic component of optically complex natural waters.
PHYTOPLANKTONPHYTOPLANKTONPhotosynthesisPhotosynthesis
Ocean ColorOcean Color
chloroplast material
cell wall
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INHERENT OPTICAL PROPERTIES
Pure Seawater Phytoplankton
b w10
-2m
-1
b w10
-2m
-1
bw, Morel (1974)aw, Pope and Fry (1997)
bchl,Loisel and Morel (1998)achl, Sathyendranath et al. (2001)
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Different pigments absorb at different wavelengths
1
1.5
2
2.5
3
3.5
4
Per
cent
Ref
lect
ance
clear water algae-laden
water
Percent reflectance of clear and algae-laden water based on in situ spectroradiometer measurement. Note the strong chlorophyll a absorption of blue
400 500 600 700 800 9000
0.5
1
Wavelength (nm)
20
25
nce
a.
500 mg/l
A lgae-Laden Water with Various Suspended Sediment Concentrations
Percent reflectance of algae-
light between 400 and 500 nm and strong chlorophyll aabsorption of red light at approximately 675 nm
5
10
15
Per
cent
Ref
lect
an
400 500 600 700 800 9000
Wavelength (nm)b.
0 mg/l
e ce t e ecta ce o a gaeladen water with various concentrations of suspended sediment ranging from 0 - 500 mg/l
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• Sunlight penetrates into the water column a certain photic depth (the verticaldistance from the water surface to the 1 percent subsurface irradiance level)
Spectral Response of Water as a Function of Dissolved Organic Constituents
distance from the water surface to the 1 percent subsurface irradiance level).• Phytoplankton within the photic depth of the water column consume nutrients
and convert them into organic matter via photosynthesis. This is calledprimary production.
• Zooplankton eat the phytoplankton and create organic matter.• Bacterioplankton decompose this organic matter.• All this conversion introduces dissolved organic matter (DOM) into oceanic,
nearshore, and inland water bodies.• In certain instances, there may be sufficient dissolved organic matter in the
water to reduce the penetration of light in the water column (Bukata et al.,1995).
• The decomposition of phytoplankton cells yields carbon dioxide, inorganicnitrogen, sulfur, and phosphorous compounds.
• The more productive the phytoplankton, the greater the release of dissolvedorganic matter In addition humic substances may be produced
Spectral Response of Water as a Function of Dissolved Organic Constituents
organic matter. In addition, humic substances may be produced.• These often have a yellow appearance and represent an important colorant
agent in the water column, which may need to be taken into consideration.• These dissolved humic substances are called yellow substance or Gelbstoffe
and can1) impact the absorption and scattering of light in the water column, and2) change the color of the water.
• There are sources of dissolved organic matter other than phytoplankton.• For example, the brownish-yellow color of the water in many rivers in the
northern United States is due to the high concentrations of tannin from theeastern hemlock (Tsuga canadensis) and various other species of trees andplants grown in bogs in these areas (Hoffer, 1978).
• These tannins can create problems when remote sensing inland waterbodies.
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Absorption Coefficient of CDOM at Different Stations in the Mayagüez Bay
0 8
0.9
1.0
Stat ion 1Stat ion 4Stat ion 5Stat ion 7
0.3
0.4
0.5
0.6
0.7
0.8
ag (
m-1
)
Stat ion 9Stat ion 11Stat ion 13Stat ion 15Stat ion 17Stat ion 19Stat ion 21Stat ion 23
0.0
0.1
0.2
0.3
350 400 450 500 550 600 650 700
Wavelength (nm)
Salinity vs. CDOM Absorption Coefficient (Ag 300 nm-1) Correlation During the Wet Season
5r = 0.72n = 32
2
3
4
ptio
n Co
effic
ient
at 3
00 n
m
n = 32
33.0 33.5 34.0 34.5 35.0 35.5 36.00
1Abso
rp
Salinity (ppt)
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Salinity vs. CDOM Absorption Coefficient (Ag 300 nm-1) Correlation During the Dry Season
1.1 r = 0.2130
0.6
0.7
0.8
0.9
1.0pt
ion
Coef
ficie
nt a
t 300
nm
n = 30
34.6 34.8 35.0 35.2 35.4 35.6 35.8 36.00.3
0.4
0.5
Salinity (ppt)
Abso
rp
MAIN COMPONENTS ABSORVING MAIN COMPONENTS ABSORVING LIGHT IN THE WATER COLUMNLIGHT IN THE WATER COLUMN
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TYPES OF WATERSTYPES OF WATERSBASED ON OPTICAL PROPERTIESBASED ON OPTICAL PROPERTIES
Oceanic Waters
Coastal Waters
MEASURING MEASURING THE WATER THE WATER THE WATER THE WATER
QUALITY WITH QUALITY WITH REMOTE REMOTE REMOTE REMOTE SENSORSSENSORS
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Secchi Disk
Used to measure the clarity (related withclarity (related with suspended particles) in water bodies
BIOBIO--OPTICAL PACKAGEOPTICAL PACKAGE
PumpPump
DataDataLoggerLogger
CTDCTD
ACAC--99HSHS--66
OCROCR--200200(Ed)(Ed)
pp
FluorometerFluorometer OCROCR--200200(Lu)(Lu)
Battery PackBattery Pack
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WATER COLUMN VARIABILITYWATER COLUMN VARIABILITY
SURFACE SPATIAL VARIABILITYSURFACE SPATIAL VARIABILITY
Salinity Fluorescence
Backscattering@589
Absorption@412
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OCEANOGRAPHIC BUOYSOCEANOGRAPHIC BUOYS
ONDULATING UNDERWATER VEHICLES
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AUTONOMOUS UNDERWATER VEHICLES
REMOTE SENSING REFLECTANCEREMOTE SENSING REFLECTANCE
GER
E
SUN
LoLoE d
L water
L sky
AbsorptionScattering
AbsorptionScattering L o
Therefore,
R = L0− fL
s
LsLs
Where, f=Fresnel Number (Percent of radiation reflected back into the atmosphere). At 45o angle is 0.028.
Rrs =
Ed
EdEd
GERGER--15001500
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Three typical spectral shapes of remote sensing reflectance curves found in Mayagüez Bay.
Remote Sensing Reflectance (Rrs) Remote Sensing Reflectance (Rrs) during the Dry and Rainy Seasonsduring the Dry and Rainy Seasons
Low Sediment input by Rivers High Sediment input by RiversLow Sediment input by Rivers High Sediment input by RiversRemote Sensing Reflectance (Rrs) for April 06
0.006
0.008
0.01
0.012
0.014
0.016
0.018
Rrs
(sr-1
)
A1
A2
AAA1
AAA2
Y1
High Chl-a Signal
Remote Sensing Reflectance (Rrs) During August 05
0.03
0.04
0.05
0.06
0.07
Rrs
(sr
-1)
A1
A2
AAA1
AAA2
Y1
Y2
High Sediment load
0
0.002
0.004
400 500 600 700
Waveleght (nm)
Y2
G2
0
0.01
0.02
400 500 600 700Waveleght (nm)
Y2
G1
G2
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OCEAN COLOROCEAN COLORWITHWITH
REMOTE REMOTE SENSINGSENSING
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Chlorophyll in Ocean Water
A remote estimate of near-surface chlorophyll concentration generallyconstitutes an estimate of near-surface biomass (or primary productivity) fordeep ocean (Case 1) water where there is little danger of CDOM andp ( ) gsuspended sediment contamination.
Numerous studies have documented a relationship between selected spectralbands and ocean chlorophyll (Chl) concentration using the equation:
Chl = x [L(λ1)/L(λ2)]y
Wh L(λ ) d L(λ ) th lli di t l t d l thWhere L(λ1) and L(λ2) are the upwelling radiances at selected wavelengthsrecorded by the remote sensing system and x and y are empirically derivedconstants.
For example, the most important SeaWiFS algorithms involve the use of bandratios of 443/355 nm and 490/555 nm.
Global Chlorophyll a (g/m3) Derived from SeaWiFS Imagery Obtained from September 3, 1997 through December 31, 1997
30
True-color SeaWiFS image of the Eastern U.S. on September 30, 1997
Chlorophyll a distribution on September 30, 1997
derived from SeaWiFS data
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1. Coastal Zone Color Scanner (CZCS)
SPACEBORNEOCEAN COLOR INSTRUMENTS
2. Modular Optoelectronic Scanner (MOS)
3. Ocean Color and Temperature Scanner (OCTS)
4. Sea-viewing Wide Field-of-view Sensor (SeaWiFS)
5. Ocean Color Imager (OCI)
6 Moderate Resolution Imaging Spectroradiometer6. Moderate Resolution Imaging Spectroradiometer
(MODIS)
7. Global Imager (GLI)
8. Medium Resolution Imaging Spectrometer (MERIS)
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Instrument SatelliteDates of
OperationSpatial
Resolution Swath Width
CZCS Nimbus-7 10/24/78-6/22/86 825 m 1556 km
OCEAN COLOR INSTRUMENTS
MOS IRS P3 3/21/96-Present 520 m 200 km
MOS Priroda 4/23/96-Present 650 m 85 km
OCTS ADEOS 8/17/96-7/1/97 700 m 1400 km
SeaWiFS Orbview-2 8/1/97-Present 1100 m 2800 km
OCI ROCSAT-1 1/99-Present 800 m 690 km
MODIS Terra/Aqua 12/18/99-Present 1000 m 2330 km
GLI ADEOS-2 scheduled 1000 m 1600 km
MERIS ENVISAT-1 scheduled 1200 m 1450 km
Comparison of Wavelength & Bandwidthfor Spaceborne Ocean Color Instruments
33
COASTAL ZONE COLOR SCANNER (CZCS)COASTAL ZONE COLOR SCANNER (CZCS)
34
SCANNING GEOMETRY OF THE CZCSSCANNING GEOMETRY OF THE CZCS
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CZCS BANDSCZCS BANDS
36
37
38
PROCESSING ALGORITHMSBased on Gordon et al. (1980) and Gordon et al. (1983)
The algorithm used for estimating the pigments content of the ocean from CZCS measurements involves the use of radiance ratios. The general form of the equation isthe equation is
log(C) = a + b*log[Lw(1)/Lw(2)]Where
C is the pigment concentration (mg/m^3) a,b are regression coefficients Lw(1),Lw(2) are the atmospherically corrected radiances for a pair of CZCS h lCZCS channels
For CZCS pigments processing, these channel pairs are
(443, 550 nm), for C < 1.5 mg/m^3 (520, 550 nm), for C > 1.5 mg/m^3
Monthly Composite of CZCS During September 1979Monthly Composite of CZCS During September 1979
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40
SeaSea--viewing Wide Fieldviewing Wide Field--ofof--view Sensorview Sensor
(SeaWiFS)(SeaWiFS)Band Wavelength (nm)
1 4121 4122 4433 4904 5105 5556 6707 7658 865
Phytoplankton ChlPhytoplankton Chl--aa
CZCS BANDS
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SeaWiFS ALGORITHMSSeaWiFS ALGORITHMS
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GLOBAL ESTIMATION OF PHYTOPLANKTONGLOBAL ESTIMATION OF PHYTOPLANKTONCHLOROPHYLLCHLOROPHYLL--A USING SEAWIFS DATAA USING SEAWIFS DATA
Orbview 2RECEIVING CAPABILITIESRECEIVING CAPABILITIESOF SeaWiFS AT UPRMOF SeaWiFS AT UPRM
LL--BAND ANTENNABAND ANTENNA
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COASTAL UPWELLING IN THECOASTAL UPWELLING IN THECARIBBEAN SEACARIBBEAN SEA
AVHRRAVHRRSea Surface TemperatureSea Surface Temperature
SeaWiFSSeaWiFSChlorophyllChlorophyll--aa
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Launched on May 4, 2002Launched on December 18, 1999
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Orbit: 705 km, 10:30 a.m. descending node (Terra) or 1:30 p.m. ascending node (Aqua), sun-synchronous, near-polar, circular
Scan Rate: 20.3 rpm, cross track
Swath 2330 km (cross track) by 10 km (along track at nadir)
MODIS Technical Specifications
Swath Dimensions:
2330 km (cross track) by 10 km (along track at nadir)
Telescope: 17.78 cm diam. off-axis, afocal (collimated), with intermediate field stop
Size: 1.0 x 1.6 x 1.0 m
Weight: 228.7 kg
Power: 162.5 W (single orbit average)
Data Rate: 10.6 Mbps (peak daytime); 6.1 Mbps (orbital average)
Quantization: 12 bits
Spatial Resolution:
250 m (bands 1-2)500 m (bands 3-7)1000 m (bands 8-36)
Design Life: 6 years
Primary Use Band Bandwidth1 SpectralRadiance2
RequiredSNR3
Land/Cloud/AerosolsBoundaries
1 620 - 670 21.8 128
2 841 - 876 24.7 201
Land/Cloud/AerosolsProperties
3 459 - 479 35.3 243
4 545 - 565 29.0 228
MODIS BANDSMODIS BANDS
5 1230 - 1250 5.4 74
6 1628 - 1652 7.3 275
7 2105 - 2155 1.0 110
Ocean Color/Phytoplankton/Biogeochemistry
8 405 - 420 44.9 880
9 438 - 448 41.9 838
10 483 - 493 32.1 802
11 526 - 536 27.9 754
12 546 - 556 21.0 750
13 662 - 672 9.5 910
14 673 - 683 8.7 1087
15 743 - 753 10.2 586
16 862 - 877 6.2 516
AtmosphericWater Vapor
17 890 - 920 10.0 167
18 931 - 941 3.6 57
19 915 - 965 15.0 250
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Primary Use Band Bandwidth1 SpectralRadiance2
RequiredNE[delta]T(K)4
Surface/CloudTemperature
20 3.660 - 3.840 0.45(300K) 0.05
21 3.929 - 3.989 2.38(335K) 2.00
22 3.929 - 3.989 0.67(300K) 0.07
MODIS BANDSMODIS BANDS
( )
23 4.020 - 4.080 0.79(300K) 0.07
AtmosphericTemperature
24 4.433 - 4.498 0.17(250K) 0.25
25 4.482 - 4.549 0.59(275K) 0.25
Cirrus CloudsWater Vapor
26 1.360 - 1.390 6.00 150(SNR)
27 6.535 - 6.895 1.16(240K) 0.25
28 7.175 - 7.475 2.18(250K) 0.25
Cloud Properties 29 8.400 - 8.700 9.58(300K) 0.05
Ozone 30 9.580 - 9.880 3.69(250K) 0.25
Surface/Cloud 31 10.780 - 11.280 9.55(300K) 0.05Surface/CloudTemperature
31 10.780 11.280 9.55(300K) 0.05
32 11.770 - 12.270 8.94(300K) 0.05
Cloud TopAltitude
33 13.185 - 13.485 4.52(260K) 0.25
34 13.485 - 13.785 3.76(250K) 0.25
35 13.785 - 14.085 3.11(240K) 0.25
36 14.085 - 14.385 2.08(220K) 0.35
Standard MODIS AlgorithmStandard MODIS AlgorithmOC3M MODIS OC3M MODIS ChlorChlor--aa
)403165904571753228300( 432 RRRR
)550490R
550443(RlogR
)403.1659.0457.1753.22830.0(10
103M
43
33
233
>=
−++−=
where
RRRRC MMMM
47
Standard MODIS ChlorophyllStandard MODIS Chlorophyll
SeaSeaSurfaceSurface
TemperatureTemperature(Celsius Degree)(Celsius Degree)
PhytoplanktonPhytoplanktonChlorophyll-a
(mg m^3)
48
Weekly Ocean Net Primary ProductivityWeekly Ocean Net Primary Productivity
PHYTOPLANKTON ROLE INPHYTOPLANKTON ROLE INTHE CARBON CYCLE?THE CARBON CYCLE?