www.elsevier.com/locate/rse
Remote Sensing of Environm
Surface mineral mapping at Steamboat Springs, Nevada, USA,
with multi-wavelength thermal infrared images
R. Greg Vaughan a,*, Simon J. Hook b, Wendy M. Calvin a, James V. Taranik a
aDepartment of Geological Sciences, University of Nevada Reno, United StatesbJet Propulsion Laboratory, California Institute of Technology, Pasadena, CA, United States
Received 14 September 2004; received in revised form 13 April 2005; accepted 28 April 2005
Abstract
The purpose of this study was to evaluate the use of airborne multispectral and hyperspectral thermal infrared (TIR) image data for
mapping surface minerals characteristic of active geothermal systems. TIR image data from the MASTER multispectral spectrometer and the
SEBASS hyperspectral spectrometer were acquired over Steamboat Springs, Nevada, USA, in September 1999. Spectral emissivity
information was extracted from the data and used to generate mineral maps. Using the MASTER data it was possible to map the extent of the
active geothermal area as well as silica-rich vs. clay-rich areas. Using the SEBASS data the same areas could be mapped and additionally the
presence of several minerals, including opal, quartz, alunite, anorthite, albite, and kaolinite could be identified. The SEBASS data also
detected previously unidentified hydrous sulfate minerals (tamarugite and alunogen) forming around active fumaroles. Laboratory spectral
data and XRD analyses of field samples confirmed the dominant mineral phases identified remotely. The airborne, field and laboratory data
together with temperature anomaly and fumarole location data from other studies were synthesized and linked to the surface geology to
determine the diagnostic surface mineral expression that could be mapped with TIR remotely sensed data for future exploration for similar
geothermal systems. Opaline sinter deposits are the most diagnostic surface expression of hot spring activity at Steamboat Springs because
they represent areas of the recent geyser activity. The differentiation between opal and chalcedony deposits and the identification of hydrous
sulfate minerals forming around active fumaroles are also important because chalcedony represents ancient sinter deposits and hydrous
sulfate minerals indicate locations of fumaroles that may be venting diffusely with no geyser activity. The surface expression of the
geothermal system at Steamboat Springs is small, which emphasizes the need for high spatial resolution airborne imagers. The 90-m pixels of
ASTER TIR data over the same area were only capable of resolving the area of past and recent sinter deposits together. MASTER
multispectral TIR data covered the entire area (¨12 km2) at 5-m spatial resolution and were capable of defining the extent of the sinter
deposits and zones of hydrothermally altered rocks. The SEBASS image swath was too narrow (256 m) to add significant spatial information
to the overall map, but the high spectral content identified several important minerals related to the local geology and the mineralogic surface
expression of the geothermal system.
D 2005 Elsevier Inc. All rights reserved.
Keywords: Thermal infrared; Multispectral; Hyperspectral; Emissivity; Mineral mapping; Geothermal exploration
1. Introduction
Airborne imaging spectrometers fill an important niche
for small- to intermediate-scale geologic remote sensing
research that compliments the global-scale data sets of
0034-4257/$ - see front matter D 2005 Elsevier Inc. All rights reserved.
doi:10.1016/j.rse.2005.04.030
* Corresponding author.
E-mail address: [email protected] (R.G. Vaughan).
satellite sensors. This study evaluates the use of thermal
infrared (TIR) remote sensing instruments for geothermal
resource exploration in Nevada, USA. Nevada is considered
to have the largest untapped geothermal resources in the
United States (http://www.eere.energy.gov/geothermal) and
Steamboat Springs is one of only nine active geothermal
systems in Nevada that is currently producing geothermal
power. Recent US Department of Energy initiatives com-
mitted to developing geothermal resources in the western
ent 99 (2005) 140 – 158
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 141
US emphasize the importance of characterizing and
identifying both known and yet-to-be-discovered geother-
mal resource targets. Specifically, this study seeks to
identify the mineralogic surface expression that is diagnostic
of an active geothermal system like Steamboat Springs and
determine the important indicator minerals that can be
mapped by TIR remote sensing tools in the exploration for
similar geothermal systems.
The TIR spectral range (8–12 Am) is widely used in
terrestrial and planetary geologic studies to map surface
minerals. Instruments that are sensitive to TIR wave-
lengths can measure known spectral features that are
related to the fundamental vibrational frequencies of
interatomic bonds within common rock-forming minerals
(Abrams, 2000; Kahle & Goetz, 1983; Kahle & Rowan,
1980; Hook et al., 1999; Rowan & Mars, 2003). Surface
mineral groups that have been mapped using TIR spectral
measurements include carbonate, sulfate, phosphate, and
felsic vs. mafic silicate minerals (Crowley & Hook, 1996;
Gillespie et al., 1984; Kahle et al., 1988; Kahle & Goetz,
1983; Ramsey et al., 1999; Sabine et al., 1994). These
0.8
0.9
0.9
Em
issi
vity
(of
fset
for
clar
ity)
Wavelength (µm)8 9 10 11 12
Albite
Quartz
Hedenbergite
Muscovite
Actinolite
Fayalite
1.0
0
1.0
0.9
0.5
0.6
0.95
0.85
0.9
1.0
A
Fig. 1. A. TIR spectra of silicate minerals. Spectral features are related to Si–O
wavelengths with increasing isolation of SiO4 tetrahedra. B. TIR spectra of other m
are reproduced from the ASTER spectral library and the ASU thermal emission sp
spectroscopy laboratory for this study. Emissivity values are scaled and offset for
studies utilized airborne TIR measurements, which were
typically only available at a few locations. Recently,
satellite instruments were launched with similar spectral
capabilities but lower spatial resolution, including the 90-
m spatial resolution Advanced Spaceborne Thermal
Emission and Reflection Radiometer (ASTER) and the
1-km spatial resolution Moderate Resolution Imaging
Spectroradiometer (MODIS) instruments (Abrams, 2000;
Salomonson et al., 1989). In addition to the new satellite
instruments, new airborne instruments have been devel-
oped, including the MODIS and ASTER airborne simu-
lator (MASTER) and the Spatially Enhanced Broadband
Array Spectrograph System (SEBASS), which are able to
make higher spatial and spectral resolution measurements
than their airborne predecessors such as the Thermal
Infrared Multispectral Scanner (TIMS). These instruments
provide new tools for remotely mapping minerals that are
important to geothermal resource exploration, which are
typically exposed on small scales that require higher
spatial resolution data than can currently be provided by
space borne sensors.
8 9 10 11 12Wavelength (µm)
Gypsum
Alunite
Kaolinite
Vegetation
Calcite
Montmorillonite
Opal
1.0
1.0
0.9
.95
0.9
0.8
0.7
0.8
1.0
0.9
0.8
0.8
0.9
B
stretching vibrations within the silicate crystal structure and shift to longer
inerals and vegetation common to the Steamboat Springs area. All spectra
ectral library except for the opal spectrum, which was measured at the JPL
clarity.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158142
2. Physical basis for thermal infrared spectroscopy
Primary rock-forming minerals as well as many secon-
dary weathering and alteration minerals exhibit wavelength-
dependent (spectral) absorption features throughout the
visible and infrared wavelength ranges of the electro-
magnetic spectrum. These features result from the selective
absorption of photons with discrete energy levels and are
dependent on the elemental composition, crystal structure,
and chemical bonding characteristics of a mineral, and are
therefore diagnostic of mineralogy (Burns, 1993; Clark,
1999; Hunt, 1980). In silicate, carbonate and sulfate
minerals fundamental molecular vibrations cause strong
spectral features that appear as emissivity minima (reflec-
tance maxima) in the 8–12 Am region (Hook et al., 1999;
Salisbury, 1993). This region coincides with a window
where Earth’s atmosphere is relatively transparent to TIR
radiation and is also the region of maximum emission from
a 300 K body (e.g., Earth), making it ideal for terrestrial
geologic remote sensing applications (Kahle et al., 1993).
For silicate minerals the wavelength position of the
emissivity minima (‘‘reststrahlen bands’’) shifts to longer
wavelengths with the increasing isolation (decreasing
polymerization) of tetrahedral SiO4 molecules in the crystal
structure (Farmer, 1974; Hook et al., 1999). The spectral
Nevada
Steamboat Springs, NV
MASTER
SEUS
Fig. 2. Map showing the location of Steamboat Springs, Nevada. Also shown are t
analyzed in this study.
features illustrated in Fig. 1 are for minerals that occur in
felsic to mafic igneous rocks, hydrothermally altered rocks,
and the mineral deposits present in the study area. For
example, a strong double emissivity minimum occurs in
quartz between 8.2 and 9.2 Am (Fig. 1A) with a character-
istic peak at 8.62 Am; a narrower emissivity feature for opal
(Fig. 1B), centered on 9.0 Am distinguishes opal from quartz
(Michalski et al., 2003).
Fundamental vibration modes for the CO32� ion occur
throughout the TIR region, and in carbonate minerals the
most distinguishing feature occurs around 11.3 Am (Fig.
1B). Measurable variations in the wavelength position of this
feature result from cation substitution in carbonate minerals
and are diagnostic of mineralogy (Lane & Christensen,
1997; White, 1974). Fundamental modes for the SO42�
ion also occur in the TIR region and cation substitution in
sulfate minerals can cause the location of resultant spectral
features to occur anywhere between 8.1 and 10.4 Am (Ross,
1974). For example, the strongest spectral emissivity feature
for alunite occurs around 9.0 Am and secondary features
occur at 8.58 and 9.75 Am (Fig. 1B). The TIR spectra of
some types of vegetation display weak emissivity features
due to organic compounds like cellulose and lignin, but have
very high emissivity values and low spectral contrast
(Salisbury & D’Aria, 1992). Combined with canopy
N1 km
BASS
39.317o N
119.
715o
W
US
395431
Geologic Map in Fig. 3
he outlines of the MASTER and SEBASS airborne remote sensing data sets
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 143
scattering, which further reduces spectral contrast, vegeta-
tion in general behaves like a blackbody emitter (Fig. 1B)
(Salisbury & D’Aria, 1992).
3. Location and geology of study area
Steamboat Springs is an active geothermal system about
16 km south of Reno, Nevada, USA (Fig. 2). It is
characterized by exposures of siliceous sinter deposits,
hydrothermally altered country rock, and structurally
controlled open fissures venting H2S-rich steam. The
geologic map (Fig. 3) is simplified from Bonham and
Rogers (1983) and Bonham and Bell (1993). The active
thermal area is about 5 km2 and lies near the northeastern
end of Steamboat Hills, coincident with a northeast
Map Color Legend
Hot Springs Sinter: Siliceous sinter depositscomposition, and ranging in age from late P
Steamboat Hills Basaltic Andesite: Basaltic plagioclase, olivine, and sparse pyroxene, ~
Granodiorite: Medium-grained granodiorite hornblende, biotite. Argillized and acid-leachLate Cretaceous in age.
Gardnerville Formation: Metavolcanic and Mage.
Undifferentiated Alluvial Deposits
Steamboat Roads
Qal
sr
Tsb
Mzvs
Kgd
Qal
Qal
Tsb
Kgd
Mzvs
Kgd
Tsb
Tsb
To Lake Tahoe
Kgd
Faults Fissures
N 1 km
Fig. 3. Simplified geologic map of Steamboat Springs (from
trending line of four rhyolite domes, which may be related
to the uplift of Steamboat Hills and to the hydrothermal
alteration of subsurface rocks (Hudson, 1987; White et al.,
1964). The basement is composed of early Mesozoic
(Triassic?) metamorphic rocks (labeled Mzvs in Fig. 3) and
Cretaceous granodiorite (Kgd). The oldest hot-spring sinter
(sr) was deposited about 3 Ma, prior to the extrusion of the
Steamboat Hills basaltic andesite (Tsb) 2.5 Ma, and the
emplacement of the Steamboat Hills rhyolite domes (not
shown on geologic map in Fig. 3) from 1.14 to 3.0 Ma
(Silberman et al., 1979). Sinter deposits are interlayered
with Pleistocene alluvium (Qal), and sinter deposition has
continued to the present. Thermal activity has been
intermittent since the late Pliocene, but nearly constant
for the past 0.1 my, varying only in magnitude (White,
1981).
ranging from chalcedony to opal in liocene to present.
andesite flows with phenocrysts of 2.5 Ma.
with Na-plagioclase, microcline, quartz, ed in the Steamboat Springs area.
etasedimentary Rocks. Triassic? in
Ditch
sr
Mzvs
Kgd
Kgd
Tsb
sr
fissures
To Reno
Qal
US
395
Steambo
at Hills
US 431
Bonham & Bell, 1993; Bonham & Rogers, 1983).
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158144
The Steamboat Springs system is a modern analog to
ancient hydrothermal systems associated with epithermal
precious metal deposits throughout the Great Basin of the
western United States (Hudson, 1987; White, 1981; White
et al., 1964). This hydrothermal system is notable for the
transport and deposition of anomalous concentrations of Hg,
Au, Ag, Sb, As, Tl, B, and S. Recent sinter deposits are
composed of opaline silica, which transforms to h-cristo-balite and chalcedony with increasing depth and age
(Hudson, 1987). Also, as a result of the remote mineral
mapping from this study, hydrous Na–Al sulfate crusts
(tamarugite and alunogen) have been discovered forming
around some active fumaroles. In the subsurface, sulfuric
acid (H2SO4) solutions produced by H2S reaction with
atmospheric O2 above the water table leaches the surround-
ing rock leaving opal, quartz, or quartz+alunite, adularia or
kaolinite/montmorillonite alteration assemblages. These
minerals are characteristic of a steam-heated acid sulfate
type alteration system (Rye et al., 1992) and are exposed at
the surface locally as outcrops of argillized and acid-leached
granodiorite and basaltic andesite.
4. Instrumentation and data collection
Table 1 is a list of the remote sensing instruments used to
collect data over the study area. The Advanced Spaceborne
Thermal Emission and Reflection Radiometer (ASTER)
was built by the Japanese Ministry of International Trade
and Industry and included on the Terra satellite, launched
by NASA in December 1999 (Abrams, 2000; Yamaguchi et
al., 1998). The ASTER level 1b at-sensor radiance data
used in this study were acquired over Steamboat Springs
in June 2001. The MODIS–ASTER airborne simulator
(MASTER) was designed by the NASA Ames Research
Center and JPL to simulate the MODIS and ASTER instru-
ments on board the Terra satellite (Hook et al., 2001). The
Spatially Enhanced Broadband Array Spectrograph System
(SEBASS) is an airborne hyperspectral imaging spectrom-
eter designed by Aerospace Corporation (Hackwell et al.,
Table 1
Instrumentation used to collect data over the study area
Instrument Spectral range (Am)* # of channels S
MASTER1 0.4–2.4 25
3.1–5.2 15
7.8–12.9 10 4
SEBASS2 3.0–5.0 128
7.5–13.5 128
ASTER3 0.55–0.81 3
1.65–2.4 6
8.3–11.3 5 3
* – Only data within the 8–12 Am TIR spectral range were used.
** – Calculated from image data.
1 – MODIS/ASTER Airborne Simulator (http://masterweb.jpl.nasa.gov).
2 – Spatially Enhanced Broadband Array Spectrograph System, Aerospace Corp
3 – Advanced Spaceborne Thermal Emission and Reflection Radiometer (http://
1996). Both MASTER and SEBASS data were acquired
over Steamboat Springs in September 1999.
The remote identification of a material based on its TIR
emissivity spectrum requires access to the spectra of well-
characterized specimens. Laboratory spectral measurements
from reference spectral libraries, as well as new measure-
ments of field samples were used to compare to the remote
spectral measurements for mineral identification. TIR
spectral data are available from the ASTER spectral library
and the ASU spectral library (http://tes.asu.edu/speclib). All
ASTER library measurements in this study were measured
as directional hemispherical reflectance and converted to
emissivity via Kirchhoff’s law (e =1� r) (Salisbury et al.,
1994). All ASU measurements were measured in emission
using heated samples (Christensen et al., 2000; Ruff et al.,
1997). New directional hemispherical laboratory spectral
measurements of field samples were made for some
minerals and mineral mixtures that were not already
available in reference spectral libraries using the same
procedure used for the ASTER library spectra (http://
speclib.jpl.nasa.gov).
Field sites for the validation of the remotely derived
mineral maps were chosen by locating areas in the images
that were representative of the mineralogic diversity of the
area and also relatively free of vegetation, and thus clearly
measured by the remote sensing instruments. Finally, X-ray
diffraction (XRD) analyses of bulk rock and mineral
separate samples were performed at two different laborato-
ries for mineralogical verification.
5. Data processing and mineral mapping methods
The methods summarized by the flow chart in Fig. 4
were used to extract the desired spectral emissivity
information from the airborne multi-channel TIR images.
The first step is the atmospheric correction of at-sensor
radiance to calculate at-surface radiance (described in
Section 5.1). At-surface radiance was then used in two
ways to extract information that could be related to the
pectral bandpass NEDT Spatial resolution/swath
40 nm 5 m/3.7 km
50–60 nm 5 m/3.7 km
00–700 nm �0.3 K** 5 m/3.7 km
2 m/256 m
35–65 nm �0.3 K** 2 m/256 m
60–100 nm 15 m/60 km
30–100 nm 30 m/60 km
50–700 nm �0.3 K 90 m/60 km
oration (http://www.aero.org).
asterweb.jpl.nasa.gov).
At-Sensor Radiance
At-Surface Radiance
TemperatureSpectral Emissivity
Atmospheric Correction
Temperature-Emissivity Separation
Decorrelation Stretch
MNF
PPI
nDv
SAM/MF
Mineral MapSynthesized Map
Spatial Information from different sources related to the geology
Field Observations
Spe
ctra
l Dat
a P
roce
ssin
g
Fig. 4. Flow chart illustrating data processing methods.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 145
composition of surface materials: 1) a decorrelation stretch
(DCS) (Gillespie et al., 1986) and 2) temperature-emissivity
separation (TqS) (Gillespie et al., 1998). Spectral emissivity
data, particularly for hyperspectral data sets, often contain a
surplus of information about the surface, as well as remnant
noise. Therefore a minimum noise fraction (MNF) trans-
formation was used to minimize noise and reduce the
overall data dimensionality (Boardman & Kruse, 1994;
Green et al., 1988; Kruse & Huntington, 1996). Spectral end
member pixels were then chosen from within the image and
used to generate pixel classification maps (Boardman, 1993;
Boardman et al., 1995). Next, minerals and mineral
assemblages within the mapped end member regions were
identified by comparison to reference spectra of pure
minerals and newly measured laboratory spectra. Finally,
the spatial distribution of spectrally mapped minerals was
combined with other spatial information from the DCS
images, field observations, and other mapping studies to
generate a mineral map that could be related to the local
geology and mineralogic surface expression of the geo-
thermal system at Steamboat Springs.
5.1. Atmospheric correction
In the TIR region, the measured at-sensor radiance
(Lm(T,k)), for a given pixel, is the sum of atmospheric path
radiance (Lp(T,k)) and upwelling at-surface radiance (Ls(T,k)),
which is attenuated by atmospheric absorption (s(k)):
Lm T ;kð Þ ¼ Ls T ;kð Þ T s kð Þ þ Lp T ;kð Þ ð1Þ
where T is temperature, k is wavelength, s(k) is atmospheric
transmittance as a function of wavelength, Lp(T,k) is
atmospheric path radiance as a function of temperature
and wavelength, and Ls(T,k) is upwelling at-surface radiance
as a function of temperature and wavelength (Gu et al.,
2000). The upwelling at-surface radiance (Ls(T,k)) is a
combination of surface emitted radiance and surface
reflected radiance and can be expanded into Eq. (1) to yield:
Lm T ;kð Þ ¼ e kð Þ T Wbb T ;kð Þ þ 1� e kð Þ� �
T Lsky T ;kð Þ� �
T s kð Þ
þ Lp T ;kð Þ ð2Þ
where e(k) is emissivity, as a function of wavelength;
Lsky(T,k) is reflected down-welling sky radiance, as a
function of temperature and wavelength, and Wbb(T,k) is
the Plank blackbody function, as a function of temperature
and wavelength (Gu et al., 2000; Hook et al., 1992).
5.1.1. MASTER
For MASTER, the MODTRAN radiative transfer model
(Berk et al., 1989) was used to atmospherically correct the
TIR at-sensor radiance to at-surface radiance. The MOD-
TRAN model uses atmospheric profile data to calculate the
atmospheric parameters (s(k), Lp(T,k)) so that Eq. (1) can be
solved for at-surface radiance (Ls(T,k)). It also calculates
reflected down-welling sky radiance values (Lsky(T,k)) that
are used in the TqS method described in Section 5.2.
Atmospheric profile data were obtained from the National
Center for Environmental Prediction (NCEP). NCEP pro-
duces global atmospheric profile models on a 1- by 1- gridat 6-h intervals. Since the study area did not reside at a grid
node, the surrounding data were interpolated to the
appropriate time and location of the data acquisition. The
interpolated profile together with the acquisition parameters
were used to run MODTRAN twice; once with a nadir
looking geometry, and once for the case of viewing at the
maximum deflection angle from nadir. Values of trans-
mittance and path radiance were calculated for each pixel in
the scene by interpolation, where it was assumed that each
quantity varies linearly with path length. The upwelling at-
surface radiance was then computed using Eq. (1).
To assess the accuracy of the atmospheric correction, the
temperature values from a homogenous area with a known
emissivity and assumed constant temperature were
extracted. Similar studies have used a body of water for
this purpose; however there was no water in this scene, so
an area of thick vegetation, which has a known and
constant spectral emissivity was used instead (Hook et al.,
1992; Hook et al., 2001; Sabine et al., 1994). The area used
consisted of a dense grove of conifers on a north-facing
slope; the emissivity for conifers was taken from the
ASTER spectral library and convolved to the MASTER
TIR channel widths. Ideally, the atmospheric correction
would result in constant kinetic temperatures calculated for
each channel; however a temperature variation for the
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158146
homogenous area after atmospheric correction was
observed to be <4 -C across all 10 channels. Channel 41
(7.8 Am) and channel 50 (12.8 Am) are both strongly
influenced by atmospheric water absorption and difficult to
correct accurately. For channels 42–49 the temperature
variation for the homogenous area was observed to be <1.5
-C. Spread in these temperature values may still be
attributed to incomplete atmospheric modeling or possibly
to true temperature variations in the grove of conifers
measured.
5.1.2. SEBASS
For the SEBASS data the Aerospace Corporation
developed an ‘‘In-Scene Atmospheric Compensation’’
(ISAC) algorithm to correct at-sensor radiance (Lm(T,k)) to
at-surface radiance (Ls(T,k)). The ISAC algorithm is
described in detail by Johnson (1998), Young (1998) and
Young et al. (2002), and is briefly reiterated by Cudahy et
al. (2000), Kirkland et al. (2001), and Vaughan et al.
(2003). In the ISAC method all atmospheric parameters
(s(k), Lsky(T,k), and Lp(T,k)) were assumed to be homoge-
neous across the image (i.e. independent of pixel location).
Furthermore, some of the pixels in the scene were assumed
to be blackbodies (e =1) (Johnson, 1998). To determine the
blackbody pixels, the at-sensor radiance data were con-
verted to brightness temperature for each wavelength
channel. Each spectrum was then searched for the wave-
length of its maximum brightness temperature and the
wavelength with the ‘‘most hits’’ was selected as a
reference wavelength. Pixels whose maximum brightness
temperature occurred at this reference wavelength were
selected as the blackbody pixels. For these pixels e =1 and
there is no reflected down-welling sky radiance (Lsky(T,k));
thus Eq. (2) reduces to Eq. (1), which shows a linear
relationship between at-sensor radiance and at-surface
radiance (Johnson, 1998). A plot of at-sensor radiance vs.
the Planck radiance function for the blackbody pixels
produces a linear scatter plot where a straight line fit to the
upper edge of the scatter distribution has a slope equal to
the atmospheric transmittance (s(k)), and an offset that is
equal to the upwelling atmospheric path radiance (Lp(T,k)).
Spread in the scatter plot is attributed to non-unity
emissivity and fitting a line to the upper edge of the data
distribution minimizes these effects (Cudahy et al., 2000;
Young et al., 2002). The at-surface radiance was then
calculated from Eq. (1).
5.2. Decorrelation stretch and temperature-emissivity
separation
Thermal infrared at-surface radiance is a function of both
the temperature and emissivity of the surface, which
commonly exhibit small variations among geologic materi-
als on the Earth’s surface, resulting in a high degree of
correlation between TIR channels. The decorrelation stretch
(DCS) in an image enhancement method that displays
emissivity variations (and corresponding mineralogic varia-
tions) as differences in color, and temperature variations
(mainly due to topography) as differences in brightness
(Gillespie et al., 1986). The DCS has been widely used with
data from other TIR instruments, e.g., TIMS (Hook et al.,
1998; Kahle, 1987; Kahle et al., 1988; Ramsey et al., 1999;
Sabine et al., 1994).
Rather than merely enhancing emissivity information, the
temperature–emissivity separation (TeS) method provides a
way to extract the emissivity component of the data. The
emissivity information was extracted from the MASTER
TIR data using the TqS technique described by Gillespie et
al. (1998). This technique uses an emissivity normalization
algorithm to estimate a temperature, from which emissivities
are calculated and ratioed to their mean (Gillespie et al.,
1998). The residual spectrum has the proper shape, but not
the correct amplitude, of the actual emissivity spectrum. For
each pixel, the minimum–maximum difference (MMD) of
the residual spectrum is used to determine the actual
emissivity spectrum by comparison to a ‘‘emin vs. MMD’’
calibration curve developed from laboratory spectra. The
calibration curve developed by Gillespie et al. (1998) was
for the ASTER instrument, and since the MASTER
channels are different, a different calibration curve was
developed for MASTER (Hook et al., 2005). The TqSalgorithm then iteratively removes reflected down-welling
sky radiance (Lsky(T,k)), which was calculated by the
MODTRAN atmospheric correction, to obtain the surface
emissivity (Eq. (2)).
Temperature and emissivity separation is a challenge for
multi-channel TIR sensors because radiance measured by an
instrument with n channels will have n +1 unknowns (n
emissivities, and 1 temperature), making the solution
equations underdetermined (Gillespie et al., 1998; Kealy
& Hook, 1993). Although in theory this is also under-
determined for hyperspectral data, the large number of
continuous narrow channels mimics the Planck radiance
function for a single temperature and provides a good
baseline for regions where e is close to 1. The SEBASS at-
surface radiance data were converted to apparent emissivity
using an emissivity normalization routine (Kealy & Hook,
1993; Vaughan et al., 2003). The spectrum for each pixel
was converted to brightness temperature, and at the wave-
length of maximum brightness temperature the emissivity
was set to 0.96 (Kealy & Hook, 1993). The resultant
emissivity spectra have a generally low spectral contrast
(overall feature depth); this is largely due to the lack of
correction for down-welling sky radiance (Lsky(T,k)) by the
ISAC method (Cudahy et al., 2000). Because the rest-
strahlen bands reflect most at the wavelengths where they
emit least, emissivity minima tend to be ‘‘filled in’’ by
reflected down-welling sky radiance, which reduces spectral
contrast (Salisbury & D’Aria, 1992).
In addition to low spectral contrast, many ISAC-
corrected at-surface radiance spectra have remnant atmos-
pheric features such as the overall spectral down slope
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 147
below 8.2 Am due to strong atmospheric absorption, and the
channel-to-channel saw-tooth pattern (particularly below 9.0
Am and above 11 Am) due to narrow atmospheric absorption
bands in this region (Cudahy et al., 2000; Hewson et al.,
2000; Vaughan et al., 2003; Zhengming & Zhao-Liang,
1997). To account for the observed spectral down slope
below 8.2 Am, the SEBASS emissivity data were fit with a
convex hull (Cudahy et al., 2000), or continuum function,
and divided by that function to remove the continuum. The
upper hull fit does not, however, remove the narrow,
remnant atmospheric features, which can overlap with
secondary mineralogic features. For example, the saw-tooth
pattern evident below 9 Am sometimes makes it difficult to
resolve the 8.62 Am peak within the characteristic quartz
doublet, and the narrow features around 12.50 and 12.77 Amcan be confused with quartz secondary features near these
wavelengths. To account for the narrow atmospheric
features, a spectral smoothing function was applied to the
continuum-removed emissivity data. Essentially a three-
point running mean, this process reduces channel-to-channel
noise without significantly affecting spectral emissivity
information that is diagnostic of mineralogy (Vaughan et
al., 2003). These processing steps can result in shifts in the
position of some emissivity features; however these slight
shifts are insignificant relative to the broad emissivity
features of minerals and thus should not affect the mineral
mapping results.
5.3. Pixel classification and spectral mineral mapping
There is a series of processing steps that has become
standard in remote sensing data analysis that yields
reproducible results (Kruse et al., 1999; Kruse et al.,
2003; Kruse & Huntington, 1996). These methods, shown
in Fig. 4, can be summarized by: 1) Minimum Noise
Fraction (MNF) transformation to minimize noise and
reduce data dimensionality, 2) Pixel Purity Index (PPI)
calculation to locate spectrally unique pixels, 3) n-dimen-
sional visualization to define spectral end members, and 4)
Spectral Angle Mapper (SAM) and Matched Filtering (MF)
methods for pixel classification and mapping of spectral end
members. The purpose of this methodology is to focus only
on the information that is relevant to characteristic
mineralogic features within the image.
The MNF transformation is a statistical operation based
on two principle components transformations that estimate
noise in the data and output a new set of channels arranged
in the order of decreasing noise components (Boardman &
Kruse, 1994; Green et al., 1988; Kruse & Huntington,
1996). With the SEBASS data, the MNF transformation was
applied to a total of 72 channels of the continuum-removed
and smoothed emissivity data that correspond to wave-
lengths 8.3–12.0 Am. This eliminates channels associated
with remnant atmospheric H2O absorption below 8.2 Amand above 12 Am. The MNF transformation produced eight
channels (MNF channels 4–11) with significant surface
compositional information. Similar to the findings of
Cudahy et al. (2000), MNF channels 1–3 show the effects
of broad instrument noise, channels 12 to ¨25 show sharp,
detector-specific noise, and channels ¨26 and higher show
random instrument/electronic noise. For the MASTER data,
with only eight emissivity channels, the MNF transforma-
tion was not necessary.
Emissivity data were used in three ways to find pixels
that represent spectral end members. First, the PPI
computation and spectral dimensionality analysis
described by Boardman (1993), Boardman et al. (1995),
and Kruse and Huntington (1996) were used to find
spectrally ‘‘pure’’ pixels (target spectra), which represent
compositionally distinct areas (Kruse & Huntington,
1996). This significantly reduces the number of pixels
that need to be searched for mineralogic spectral
information. The distribution of these points in n-dimen-
sional space was determined to define end members with
distinct spectral signatures and these end members were
used to classify other pixels in the image. The second
method was similar, except the pure pixels were chosen
manually based on analysis of the image data. Regions of
interest were defined around obvious areas of geologic
interest (e.g., non-vegetated areas) and these pixel spectra
were viewed as points in n-dimensional space to select the
outliers (apical points). This helps reduce the number of
pixels that are chosen by the automated PPI process that
are not related to geologic diversity, e.g. vegetation, roads,
and roofs. Thirdly, in some cases, spectral end member
pixels were chosen based on a priori knowledge and
sampling of the field area. In this case, just a few pixels
were selected as end member spectra to eliminate the need
for n-dimensional analysis. Each spectral end member was
used as a target spectrum, to ‘‘train’’ the pixel classi-
fication method described next.
Pixels were classified using two different supervised
classification methods: 1) Spectral Angle Mapper (SAM)
(Kruse et al., 1993) and Matched Filtering (MF) (Boardman
et al., 1995). SAM classifies pixels together based on their
spectral similarity by treating spectra as vectors in n-
dimensional space and calculating the angle between them.
The threshold angle used was 0.05 radians. MF generates
proportional spectral end member abundance maps based on
partial unmixing of image target spectra (Boardman et al.,
1995). It maps the abundances of pixels that most closely
match the target spectrum of known end members while
filtering out unmatched background pixels. For each end
member mapped, a region of interest (ROI) was defined by
selecting a range of threshold values from the abundance
maps that corresponded to the highest abundance. Each ROI
was assigned to a unique color and displayed over a gray-
scale image to produce a mineral classification map. Finally,
based on matching the spectra of classified pixels to the
spectra of pure minerals from reference libraries, mineralogy
was assigned to classified pixel regions to produce mineral
maps that will be discussed in Section 6.
Quartz
Albite
Kaolinite
Linear Mixture 1
Linear Mixture 2
0.7
0.6
0.8
0.9
1.0
Em
issi
vity
(of
fset
for
clar
ity)
8 9 10 11 12
Wavelength (µm)
0.5
Fig. 5. Example of linear mixing of pure mineral reference spectra in the
TIR wavelength region. Linear mixture 1 is 10% quartz, 45% albite, and
45% kaolinite; linear mixture 2 is 40% quartz, 30% albite, and 30%
kaolinite.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158148
5.4. Mineral mapping limitations and linear spectral mixing
Natural geologic surfaces are often partially covered with
non-geologic materials (e.g., vegetation) or composed of
mixtures of minerals with varying grain sizes and differing
degrees of compaction/solidification. These factors influ-
ence remote spectral measurements and limit the number of
pixels that can be classified and mapped. In the TIR spectral
range, decrease in particle size can increase volume
scattering and decrease the spectral contrast (overall depth)
of the reststrahlen features–unless the particles are com-
pacted sufficiently to scatter coherently, in which case the
spectral contrast remains relatively high (Salisbury & Wald,
1992). Reference spectra have been acquired for some
minerals with different grain sizes to study the effects of
grain size on spectral characteristics (e.g. Salisbury et al.,
1991). Not all minerals, however, have been subjected to
such systematic spectral characterization. Therefore, the
reference spectra used in this study are from measurements
of coarse grained (>250 Am) and solid samples, and no
attempt was made to model grain size variations based on
image spectra.
Mixing can exist at various scales and also affects the
measured infrared spectral properties of an area (Clark,
1999). Even high-spatial-resolution (2-m pixel) images can
have contributions from multiple sub-pixel-scale compo-
nents. Using TIR data, Ramsey and Christensen (1998)
showed that a linear unmixing technique that models the
percentage of each end member composition can be used to
identify individual surface minerals within a single pixel. A
similar approach was used in this study by calculating linear
mixtures of reference spectra from the ASTER and ASU
spectral libraries and plotting them with the remote and field
spectra for comparison (Vaughan et al., 2003). To begin
with, reference spectra for pure minerals were chosen based
on initial spectral analyses and knowledge of the geology
and alteration minerals expected in each study area. Then
linear combinations of these pure mineral spectra were
plotted and compared to SEBASS image spectra. Since the
broad spectral band pass of MASTER does not permit
unique mineral identification, only SEBASS emissivity
spectra were modeled by linear mixtures of reference
spectra. Fig. 5 shows examples of spectral plots for pure
minerals and the results of linear combinations. Through
visual inspection and trial and error, spectral mixtures were
matched to image spectra to identify the dominant mineral
phases present. It is important to note that the percentages of
mineral components used in the spectral mixtures do not
reflect the actual percentages of the minerals in the pixel. In
some cases, reference spectra from pure minerals and
mineral mixtures had to be scaled down to directly overlay
with the image spectra. This is a function of the generally
lower spectral contrast that appears in remotely acquired
spectra due to either grain size effects, mixing with either
non-geologic components or other minerals that have low
spectral contrast, or in the case of SEBASS, the lack of
correction for reflected down-welling radiance in the
atmospheric correction process. As a result of this semi-
quantitative treatment of linear mixtures, spectral feature
depth and absolute emissivity values were not perfectly
preserved, and no attempt was made to quantitatively model
mixtures of pure minerals to match the SEBASS spectra. As
will be shown in the next section, only spectral shapes and
feature locations were used for mineral identification and
these methods were sufficient to detect the presence of the
dominant mineralogy of mixed pixels and produce a mineral
map.
6. Results and interpretation
6.1. Decorrelation stretch
Fig. 6A shows a decorrelation stretch (DCS) image of the
90-m ASTER TIR channels 14, 13, and 12 (wavelengths
11.32, 10.66, and 9.08 Am) displayed as red, green, and blue
(RGB), respectively. With these channels, the silica-rich
sinter area around Steamboat Springs stands out as yellow in
the center of the image because silica has a low emissivity
around 9.0 Am (channel 12–blue) and higher emissivity at
10.66 and 11.32 Am (channel 13–green and channel 14–
red, respectively). For a comparison the accompanying Fig.
6B shows a false color composite of ASTERVNIR channels
golf course
sinter area
acid-sulfate area
irrigated fields
Steamboat Hills
MASTER
SEBASS
sinter area
irrigated fieldsgolf
course
Steamboat Hills
1 kmN
A
B
1 kmNFig. 6. A. ASTER TIR DCS image over Steamboat Springs. ASTER TIR
DCS channels 14, 13 and 12 are displayed as RGB, respectively. This set of
channels (different than those typically used for DCS images) more clearly
highlights differences between silica and clay. The sub-horizontal noisy
scan lines are due to the ASTER TIR scanner. The areas imaged by
MASTER and SEBASS are outlined by the rectangles. The spatial
resolution for the ASTER TIR image is 90 m. B. ASTER VNIR image
over Steamboat Springs. ASTERVNIR channels 2, 3N and 1 are displayed
as RGB, respectively. The areas imaged by MASTER and SEBASS are
outlined by the rectangles. The spatial resolution for the ASTER VNIR
image is 15 m.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 149
2, 3N, and 1 (wavelengths 0.66, 0.81, and 0.55 Am,
respectively) displayed as RGB. In this image, healthy
vegetation (e.g. irrigated fields) appears bright green, and
dry desert vegetation appears various shades of purple. The
bright, white areas correspond to the siliceous sinter area
around Steamboat Springs and an area of acid-sulfate
alteration to the west. With the 15-m pixels of the VNIR
image more detail about the region can be seen, including
roads, fields, urban areas, the sinter area and acid-sulfate
alteration area, areas with recent construction activity, a golf
course, small lakes, and healthy vegetation along stream
drainages. At the 90-m spatial resolution of the TIR
channels (Fig. 6A), the siliceous sinter area (yellow) and
large vegetated areas (dark) are the only regional spatial
features that are clearly mappable. Outlines of the high-
spatial resolution airborne images acquired by the MASTER
and SEBASS instruments are indicated with black rectan-
gles in each image.
Fig. 7A shows the DCS of MASTER channels 48, 45,
and 44 (wavelengths 11.20, 9.68, and 9.05 Am, respectively)
displayed as RGB. This channel combination was chosen to
mimic the color scheme of the SEBASS DCS (described
next). Silica-dominated regions appear yellow because silica
has a low emissivity associated with the reststrahlen band
around 9.0 Am (channel 44–blue) and high emissivity at 9.6
and 11.2 Am (channel 45–green and channel 48–red,
respectively). For example, the large yellow region on the
right side of the image represents the siliceous sinter
deposits around Steamboat Springs. The Ormat (formerly
SB Geo, inc.) geothermal power plant is located just north
of most of the recent sinter deposition (brightest yellow).
Clay-dominated areas appear magenta to purple because
clay has a low emissivity value around 9.6 Am (channel 45–
green) and higher values at 9.0 and 11.2 Am (channel 44–
blue, and channel 48–red). The low emissivity values of
clays (phyllosilicate minerals) are also associated with a
reststrahlen band but the minimum is shifted to slightly
longer wavelengths (see Fig. 1A). For example, on the left
side of the image, west of Steamboat Springs, there are a
number of areas with active urban development and the
exposed soils and dirt roads are clay-rich. In contrast,
ASTER is not capable of separating clay-rich from silica-
rich areas due to the lack of a spectral channel between 9.1
and 10.6 Am, where clay minerals have their strongest
spectral features. Healthy vegetation (trees, lawns and
fields) is dark green; for example, the sports fields around
Galena High School left center of image. Areas that appear
cyan to dark purple are generally covered by dry desert
vegetation (sagebrush and cheat grass) and are thus
spectrally featureless and indistinguishable in the TIR.
However, because differences in albedo also affect colors
in the DCS image, some geologic information can be
interpreted from the differences between cyan areas (under-
lain by variably altered granodiorite) and the darker purple
areas (underlain by basaltic andesite), e.g., the area just
southwest of the main sinter terrace. Roads appear in
various shades of purple and orange due to differences in
composition: asphalt, cement or dirt/gravel, and roofs in
urban areas appear green, blue, or yellow.
The channel combination used for all the DCS images
here is not the same combination that has commonly been
used with other multispectral TIR data, such as TIMS,
which results in silica-rich areas displayed as red and clay-
rich areas as purple (Kahle, 1987; Ramsey et al., 1999;
Sabine et al., 1994). The channel combination used here
produces a more obvious visual distinction between the
silica- and clay-rich areas that dominate the geologic
variance in this scene. Furthermore, with the hyperspectral
SEBASS data, the wavelength channels used in the DCS
Fig. 7. A. MASTER decorrelation stretch (DCS) image over Steamboat Springs displaying channels 48, 45, and 44 as RGB. This set of channels (different than
those typically used for DCS images) more clearly highlights differences between silica and clay. Color variations are related to emissivity differences, and thus
surface compositional differences; temperature variations are displayed as intensity differences. The dashed outline indicates the extent of the SEBASS data
coverage. The spatial resolution for the MASTER image is 5 m. B. SEBASS DCS image over Steamboat Springs (modified from Vaughan et al., 2003)
displaying channels 66, 45, and 44 as RGB. The color scheme is the same as for Fig. 9, additionally. The spatial resolution for the SEBASS image is 2 m.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158150
here produce a color separation of other mineral groups. The
SEBASS DCS uses channels 66, 35, and 24 (wavelengths
11.0, 9.5, and 9.1 Am, respectively) as RGB (Fig. 9). The
resultant colors are similar to those of the MASTER DCS
with silica-rich areas in yellow and clay-rich areas in
magenta, e.g., the bright yellow siliceous sinter area on the
east side of the Steamboat Springs image, and some clay-
rich (magenta) areas in the acid-sulfate alteration region to
the west. Because of the higher spectral resolution of
SEBASS, the DCS separates more compositional end
members, for example pale green areas that contain sulfates
like alunite (also in the acid sulfate alteration region). In all
the DCS images temperature variations appear as intensity
differences that look like shadows on the north-facing
slopes.
6.2. Mineral maps and emissivity spectra
Using the spectral information measured by each
airborne instrument, mineral maps were created using the
methods described in Section 5.3. In general, surface cover
types included vegetation, rock outcrop, soil, or man-made
materials such as roofs or roads. Roofs and other man-made
materials sometimes have characteristic spectral features in
the TIR spectral region, but to focus on mapping minerals
related to local geology, pixels over roads and urban areas
were not mapped. In some cases pixels were mineralogi-
cally homogenous, containing only one mineral phase
across the entire pixel (e.g., on the sinter terrace). In other
cases pixels were mineralogically heterogeneous. A pixel
that contains a mixture of different materials produces a
spectrum that represents a linear combination of each
component. As described in Section 5.4, reference spectra
for pure minerals from TIR spectral libraries were mixed
together in a linear fashion to approximate the remotely
measured SEBASS spectra and identify the presence of the
dominant mixed components. In many pixels however,
even small (2-m) pixels, contribution from non-geologic
components (primarily vegetation) adversely affected the
mineralogic spectral signature. In general, pixels dominated
by (containing >50%) non-geologic materials were not
classified and mapped. In the TIR region vegetation
approximates a blackbody with a very high emissivity that
is invariant with wavelength (Salisbury & D’Aria, 1992).
As a result, mixture with vegetation reduces the overall
spectral contrast of mineralogic spectral features within a
mixed pixel, so the presence of vegetation was not modeled
using TIR data.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 151
Fig. 8 (top) is the MASTER mineral map over Steamboat
Springs. There are two different mineralogical compositions
mapped: yellow areas are generally silica- or sulfate-rich
and represent either quartz, alunite, or opal; magenta areas
are generally clay-rich and represent either kaolinite or
montmorillonite. The silica-rich areas were classified based
on a common emissivity minimum centered around 9.1 Am,
Fig. 8. MASTER mineral map over Steamboat Springs (top). The two mapped reg
either silica-rich or clay-rich. MASTER spectra (lower plots) for selected sites (8, 1
to the map legend and compared to mineral reference spectra resampled to MASTE
The dashed outline represents the extent of the SEBASS data coverage shown in
and the clay-rich areas were classified based on an
emissivity minimum around 9.7 Am. In the spectral plots,
MASTER spectra in yellow (left) match the ASU library
reference spectra for either quartz, alunite, or opal; the
spectra in magenta (right) match the ASU library reference
spectrum for clay minerals such as kaolinite and montmor-
illonite. The spectral resolution of MASTER was not
ions are overlain onto a gray-scale temperature image, and distinguished as
1b, 12, 16, and 18–marked with triangles on the map), are color coordinated
R’s spectral resolution. Other field sites are marked with circles on the map.
Fig. 9. The spatial resolution for the MASTER image is ¨5 m.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158152
sufficient to resolve the subtle spectral differences between
the minerals within each class.
Fig. 9 shows the SEBASS mineral map of Steamboat
Springs (dashed outline in Fig. 8), which is improved over
the SEBASS mineral mapping shown in Vaughan et al.
(2003). Although it covers a very narrow swath, the spectral
resolution of SEBASS was capable of separating more
spectral end members and mapped more unique minerals
than the multispectral MASTER data. The SEBASS
spectrum in orange from the siliceous sinter area (site 8–
left spectral plot) matches the reference spectrum of opal. In
this case, due to limited samples in existing spectral libraries,
a new reference spectrum for opal was determined using
Map Color Legend
Alunite
Opal
Albite + Kaolinite + Alunite Kaolinite
Na-Al sulfate (Tamarugite/Alunogen)
Quartz
11b12
Albite + Andesine
9
21
Em
issi
vity
(of
fset
for
clar
ity)
8 10 11 12
0.7
0.8
0.9
1.0
9
Wavelength (µm)
Site 12
Site 11b
Site 8
opal
quartz
alunite
0.25 kmN
Fig. 9. SEBASS mineral map over Steamboat Springs (top) (modified from Vaug
emissivity image, and distinguished by their dominant mineralogy as noted in the
11b, 12, 19, and 21–marked with triangles on map) are color coordinated to the m
mixtures of mineral reference spectra. The spatial resolution for the SEBASS im
measurements at the JPL spectroscopy laboratory of samples
from the siliceous sinter terrace at Steamboat Springs. The
narrow emissivity minimum around 9.0 Am is characteristic
of opal and XRD analyses confirm the composition of
siliceous sinter as pure opal. The SEBASS spectrum in
yellow from the acid-sulfate alteration area (site 9–left
spectral plot) matches the ASU library reference spectrum of
quartz. The large doublet feature between 8.2 and 9.2 Amwith an emissivity peak at 8.62 Am is characteristic of
crystalline quartz. XRD analyses confirm that quartz is the
dominant mineral at this site. The SEBASS spectrum in blue
from the acid-sulfate alteration area (site 12–left spectral
plot) matches the JPL library reference spectrum of alunite.
19
8
7
Site 9
Site 7
Site 19
8 10 11 129Wavelength (µm)
Site 21
SEBASS spectra
Plot Color Legend
Reference spectra of pure minerals or linear mixtures
kaolinite
kaolinite + albite + alunite
anorthite + kaolinite
gypsum + mirabilite
han et al., 2003). The seven regions mapped are overlain onto a gray-scale
legend. SEBASS spectra (bottom, left and right) from the field sites (7, 8, 9,
ap legend and compared to reference spectra from pure minerals, or linear
age is ¨2 m.
Table 2
Minerals identified at Steamboat Springs with each instrument
Field site MASTER
(Fig. 8)
SEBASS
(Fig. 9)
Lab
spectroscopy
XRD
SS 7 ND Anorthite
Kaolinite
ND Anorthite
Albite
Augite
SS 8 Silica Opal Opal Opal
SS 9 Clay Kaolinite Feldspar Albite
Anorthite
Clay Montmorillonite
Augite
SS 11b Silica Quartz Quartz Quartz
SS 12 Silica Alunite Alunite Alunite
Quartz
Kaolinite
Opal
SS 16 Clay ND Kaolinite Kaolinite
SS 17 Silica ND Quartz
(Chalcedony)
Quartz
SS 18 Clay ND ND Kaolinite
Alunite
Quartz
Orthoclase
SS 19 Silica Sulfate Sulfate Alunogen
Tamarugite
Kieserite
SS 21 ND Kaolinite
Albite
Alunite
ND Kaolinite
Quartz
Opal
Na-alunite
Minamiite
ND=Not determined.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 153
The TIR emissivity spectrum for alunite is characterized by a
broad minimum around 9.0 Am, with secondary features at
8.57 and 9.7 Am. XRD analyses indicate the presence of
alunite, quartz, kaolinite and minor opal. The SEBASS
spectrum in magenta from an exposure of soil on top of the
Steamboat Hills basaltic andesite (site 9–right spectral plot)
matches the ASU library reference spectrum of kaolinite.
An emissivity minimum around 9.5 Am is characteristic of
many clay minerals, but the secondary features at 8.88 and
11.0 Am, and the shoulder at 9.9 Am are diagnostic of
kaolinite. XRD analyses, however, indicate the presence of
montmorillonite with minor albite, anorthite, and augite.
The SEBASS spectrum in brown is from an exposure of the
Steamboat Hills basaltic andesite (site 7–right spectral
plot). The extremely low spectral contrast makes mineral
identification more difficult; however, the emissivity
minima at 8.6 and 9.6 Am, with a shoulder at 9.9 Ammatch a linear mixture of 50% anorthite and 50% kaolinite
from the ASU spectral library. XRD analyses of unweath-
ered samples indicate the presence of albite, anorthite, and
augite; the kaolinite is present on the surface as a weath-
ering product. The SEBASS spectrum in green from the
acid-sulfate alteration area (site 21–right spectral plot) has
spectral features at 11.0, 9.9, 9.6, 9.3, and 8.8 Am, and
matches a linear mixture of ASU library reference spectra
for albite (40%), kaolinite (40%), and JPL library alunite
(20%). XRD data indicate the presence of kaolinite, quartz,
Na-alunite, minamiite (a Ca-rich alunite mineral), and
minor opal. Lastly, the SEBASS spectrum in red, from an
exposure of hydrous sulfate crusts forming around an active
fumarole (site 19–right spectral plot) has a broad emissivity
minimum around 8.8 Am, similar to many sulfate minerals.
XRD analyses indicate the presence of the hydrous Na- and
Al-sulfate minerals, tamarugite and alunogen with minor
kieserite (Mg-sulfate). These sulfate minerals have not been
characterized in any reference spectral libraries, therefore
the USGS library reference spectrum of gypsum (50%)
mixed with mirabilite (50%), another hydrous Na-sulfate
mineral, is shown for comparison.
Table 2 is a summary of the major minerals identified and
mapped at Steamboat Springs with MASTER and SEBASS
data, as well as corroboratory measurements made by
laboratory spectroscopy and XRD analyses. With the
exception of MASTER, which cannot uniquely identify
minerals, the minerals mapped remotely agree with the
dominant mineralogy determined by XRD analyses. In
some cases (sites 7, 9, 11b, 12, 18, and 19) XRD analyses of
field samples identified minor mineral constituents that were
not identified by remote spectroscopy. In other cases (sites
7, 9 and 21) there were minerals identified remotely that
were not found in the samples subjected to XRD analyses.
In all cases these discrepancies can be attributed to
differences in scale between the area covered by the remote
sensing data and the samples collects from each site. While
every effort was made to collect samples that were
representative of the larger areas viewed by the remote
images, this was not always possible, and XRD analyses of
some samples were not necessarily representative of entire
pixel area. Site 17 is notable because although it is only
mapped by the MASTER data, it is important in the
interpretation of the mineralogic surface expression of the
Steamboat Springs geothermal system. The presence of
micro-crystalline quartz (chalcedony) was only positively
identified by field sampling and laboratory analyses. Had
the SEBASS swath covered this area, it would have
differentiated between this crystalline quartz and the opal
on the sinter terrace.
6.3. Spatial data synthesis and interpretation
The active geothermal system at Steamboat Springs is
characterized by 1) opaline sinter deposits that are indicative
of recent geyser activity, 2) chalcedonic sinter deposits that
are indicative of older, but geologically recent geyser
activity, 3) hydrous Na–Al sulfate deposits that are
indicative of active fumaroles, and 4) the presence of
hydrothermally altered rocks with minerals like alunite and
kaolinite. While these hydrothermal alteration minerals may
also be indicative of ancient acid-sulfate hydrothermal
systems, their presence among the other three diagnostic
characteristics provides clues about the location and
duration of past hydrothermal activity in the area.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158154
Fig. 10 is a mineral map of the Steamboat Springs area
that combines all the mineralogic information derived from
both remote sensing data sets and field mapping showing
the surface minerals related to the local geology, and to past
and recent geothermal activity. The Steamboat Hills basaltic
andesite (Tsb–pale brown) from the geologic map in Fig. 3
is more widespread than the limited area covered by the
SEBASS image. SEBASS spectra (Fig. 9) from the areas
mapped in dark brown indicate the presence of anorthite,
which is common in basaltic andesite. The high-spatial-
resolution, hyperspectral SEBASS data were capable of
detecting the subtle spectral characteristics of the basaltic
andesite unit in between trees and bushes. Much of the area
underlain by this unit is heavily vegetated, and significant
(>50%) vegetation cover can hinder the spectral identifica-
tion of the underlying soil and rock. However, information
Fig. 10. Mineral map of the Steamboat Springs area showing the distribution of m
from the geologic map in Fig. 3 are shown in pale, partly transparent colors. The
solid, opaque colors. The extent of the overlapping SEBASS image is outlined in
derived from both MASTER and SEBASS DCS images was
also used to determine the spatial distribution of the basaltic
andesite. Although, the remotely mapped distribution of the
basaltic andesite unit is not comprehensive, there is good
agreement with respect to the spatial distribution recorded
on the original geologic map.
The Cretaceous granodiorite (Kgd–pale green) from the
geologic map is also widespread and largely hydrothermally
altered where exposed. Within the SEBASS swath, this unit
is mapped by the identification of quartz, albite, alunite and
kaolinite spectral signatures; these are the primary minerals
that compose the altered granodiorite. Outside of the
SEBASS swath the Kgd unit is mapped in areas where
MASTER detects silica-rich material and field mapping and
sampling determined the presence of altered granodiorite.
Also, in the MASTER DCS image, the cyan colored areas
inerals related to both active and past hydrothermal activity. The rock units
mineral units mapped with the remote sensing and field data are shown in
black. The spatial resolution of the DOQ in the background is ¨1 m.
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158 155
generally correspond to vegetated areas underlain by the
granodiorite unit.
Of primary importance in locating active geothermal
systems like Steamboat Springs is the location of hot spring
sinter. The spatial distribution of sinter deposits from the
geologic map (sr–pale yellow) and from the remote mineral
map (opaque yellow) is very similar. However, on the
geologic map there is no differentiation between recent
sinter, which is opal, and older sinter, which is a form of
micro-crystalline quartz called chalcedony. MASTER spec-
tral data classify these materials together, but mapping based
on field observations and sampling differentiated between
these areas. The SEBASS data were also capable of
differentiating between opal and more crystalline silica;
however the SEBASS swath did not cover the area with
older (chalcedonic) sinter.
Another characteristic of the Steamboat Springs geo-
thermal system that can be identified by TIR remote
sensing methods is the distribution of surface temperature
anomalies. Zones of anomalously high temperatures
mapped by Coolbaugh (2003) using overlapping day-time
and night-time TIMS data in conjunction with Airborne
Visible Infrared Imaging Spectrometer (AVIRIS) data, are
shown in magenta outlines in Fig. 10. Also, the locations
of known fumaroles are shown as blue squares. There are
three very small areas (annotated on the map) where the
hydrous Na–Al sulfate minerals, tamarugite and alunogen,
were mapped by the SEBASS data. These deposits
correspond to the locations of both active fumaroles and
some of the high temperature areas. Although there is a
good correlation between the occurrence of hydrous
sulfates, active fumaroles, and hot spots, it is important
to note that not all active fumaroles have sulfate forming
around their surface interface. There may be sulfates
forming at depth, or not at all. Also, since these sulfates
are water soluble, they would presumably wash away after
a rain storm and reform some time later. Questions about
the formation time, duration and ephemeral nature of these
hydrous sulfate deposits, as well as the associated micro-
bial communities will be important to address in future
studies.
With respect to surface mineral mapping for geothermal
resource exploration, the identification of sinter as an
indicator mineral is considered to be of primary importance.
The differentiation between opaline sinter and more
crystalline silica phases such as chalcedony or quartz,
which can be present in many geologic environments other
than geothermal systems, is also critical. Hydrous sulfates
and hydrothermal alteration minerals are of secondary
importance in the location of active systems. At Steamboat
Springs the current orientation of recent sinter deposits in a
generally north–south alignment (along highway 395) is the
surface expression of the structurally controlled fissures that
provide conduits for geothermal waters. Also, the presence
of older sinter to the west may indicate an eastward shift in
geyser activity with time. The characterization of structures
at depth and the mineral deposits at the surface ultimately
plays an important role in understanding the spatial/
temporal evolution of the geothermal system, and in
geothermal energy exploration.
7. Summary and conclusions
In addition to the comparison of multispectral and
hyperspectral data for spectral mineral mapping, this study
combines remote mineral mapping with field mapping data
and relates the spatial information to the local geology and
geochemical environment. For Steamboat Springs, this
study resolves questions about what geologic and minera-
logic surface characteristics are important to geothermal
energy exploration and what multi-channel infrared remote
sensing instrument parameters are necessary to map
minerals associated with active geothermal systems. This
study also represents the first direct comparison of over-
lapping multispectral and hyperspectral TIR data as well as
a unique synthesis of multiple remote and field-derived data
sets directly linked to local geology and alteration units and
focused on the identification of important indicator minerals
for geothermal exploration. It also resulted in the first
remote detection of hydrous sulfate minerals forming
around active fumaroles at Steamboat Springs.
The mineralogic surface expression of the Steamboat
Springs geothermal system consists of (1) siliceous sinter
deposits composed of opaline silica, which are indicative
of recent geyser activity, (2) massive chalcedony deposits,
which are indicative of older, but geologically recent
geyser activity, (3) hydrous Na–Al sulfate crusts forming
around active fumaroles, and (4) rocks that have under-
gone steam heated acid-sulfate alteration, which offer clues
about the location and duration of past geothermal activity.
In the exploration for similar geothermal systems opaline
sinter is the primary indicator mineral that is characteristic
of active, or recently active hot springs and can be
identified by TIR hyperspectral data. Chalcedonic sinter
deposits are also important, so it is critical to be able to
separate amorphous silica from crystalline silica phases
that could be present in a variety of geologic environ-
ments. This differentiation can be achieved remotely only
by hyperspectral TIR data or by using laboratory spectral
measurements. Hydrous sulfates are of secondary impor-
tance because they are not present around all fumaroles
and their presence is ephemeral, as they would dissolve
and wash away during a storm. These sulfate minerals can
be detected by hyperspectral TIR data, but unique
identification requires more library reference spectra for
these uncommon sulfate minerals.
It is sometimes merely presupposed that high-spatial- and
high-spectral-resolution measurements are necessary for
detailed spectro-lithologic mapping. This study has pre-
sented specific examples of the advantages of such
measurements and should be helpful in placing some limits
R.G. Vaughan et al. / Remote Sensing of Environment 99 (2005) 140–158156
on, and setting some goals for, the specifications of future
airborne and spaceborne remote sensing systems for geo-
logical applications. For example, the SEBASS mineral
mapping at Steamboat Springs illustrates that spectral
feature position and shape are more important than absolute
value and spectral feature depth for mineral identification.
These spectral parameters are best preserved at high spectral
resolution and this is the reason that hyperspectral measure-
ments can be modeled by linear mixtures of reference
spectra, and that hyperspectral instruments like SEBASS are
capable of uniquely identifying more minerals than multi-
spectral instruments like MASTER. High spatial resolution
offers the ability to image areas in between trees and bushes
reducing the negative effects of sub-pixel mixing and also
makes the data products easier to register to other maps for
spatial analysis and display. One of the most common non-
geologic components interspersed with geologic materials is
vegetation, even in the desert. In this study, pixels where
soil and rock were mixed with >50% vegetation were
generally not mappable based on mineralogic spectral
features. High spatial resolution, however, is often associ-
ated with a narrow swath (e.g. the 256 m swath of the
SEBASS image). The spatial resolution vs. swath trade-off
is an important consideration that depends on the scale of
the mapping application. The fact that wide-swath, large
spatial footprint images acquired by spaceborne systems are
best suited for global and regional scale mapping empha-
sizes the necessity of airborne instruments for more detailed
intermediate- to small-scale geologic remote sensing
research.
Acknowledgements
The research described in this paper was carried out in
part at the Jet Propulsion Laboratory, California Institute
of Technology, under contract with the National Aero-
nautics and Space Administration (NASA) as part of the
Earth Observing System, Mission to Planet Earth Pro-
gram. This work has been supported by the Nevada Space
Grant Consortium, the Arthur Brant Laboratory for
Exploration Geophysics, and NASA grant NGT5-50362
(the NASA Graduate Student Research Program Fellow-
ship). The authors would like to thank Alan Gillespie and
Mike Abrams for their constructive reviews of this
manuscript; John Hackwell and Patricia Lew at Aerospace
Corporation for the opportunity to participate in the 1999
SEBASS group shoot and for helping with raw data
reduction and implementation of the ISAC routine; Cindy
Grove and Ron Alley at the Jet Propulsion Laboratory for
providing TIR laboratory measurements of field samples
and atmospheric profile data for the calibration of
MASTER data; and Mario Desilets at the Nevada Bureau
of Mines and Geology, and Paul Schroeder at the
University of Georgia for assistance with XRD analyses
of field samples.
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