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<metadata xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:noNamespaceSchemaLocation="http://water.usgs.gov/GIS/metadata/usgswrd/fgdc-std-001-1998.xsd">
	<idinfo>
		<citation>
			<citeinfo>
				<origin>Larry D. Putnam, U.S. Geological Survey</origin>
				<pubdate>2001</pubdate>
				<title>Polygons Representing Sensitivity of Ground Water to Contamination in Lawrence County, SD</title>
				<edition>(Version 1.0, January 22, 2001)</edition>
				<geoform>Digital map</geoform>
				<pubinfo>
					<pubplace>Rapid City, SD, USA</pubplace>
					<publish>U.S. Geological Survey</publish>
				</pubinfo>
				<onlink>http://water.usgs.gov/lookup/getspatial?sd_lcsens_pol</onlink>
				<lworkcit>
					<citeinfo>
						<origin>Larry D. Putnam</origin>
						<pubdate>2000</pubdate>
						<title>
Sensitivity of Ground Water to Contamination
in Lawrence County, SD
						</title>
						<serinfo>
							<sername>Water-Resources Investigations Report</sername>
							<issue>WRIR 00-4103</issue>
						</serinfo>
						<pubinfo>
							<pubplace>Rapid City, SD, USA</pubplace>
							<publish>U.S. Geological Survey</publish>
						</pubinfo>
					</citeinfo>
				</lworkcit>
			</citeinfo>
		</citation>
		<descript>
			<abstract>
This data set includes 956 polygons labeled with a
sensitivity-unit code that represents the sensitivity of ground
water to contamination in Lawrence County, SD. This data set is a
result of a larger work (WRIR 00-4103 cited above), which
includes a paper plate titled: "Map showing sensitivity of
ground-water to contamination in Lawrence County, South Dakota."
This data set is part of the digital data that was used to create
that map.  The sensitivity-unit code is an attribute that
consists of a letter followed by three numerical digits,
which characterizes sensitivity to contamination.  Letter codes
that begin with upper case letters (A-Z) and continue with lower case
letters (a-s) represent characteristics of the rock and sediments,
with 'A' being most sensitive and 's' being least sensitive. The first
digit represents recharge rate with 1 being the most sensitive and 4
the least sensitive. Three quantitative categories (1-3) and
two qualitative categories (4,5) represent depth to water.
Groups 1 through 3 represent areas where data was available
to estimate depth-to-water with 1 most sensitive and 3 least
sensitive. Qualitative categories 4 and 5 represent areas that only
can be compared to each other with 4 being the most sensitive.
The third digit represents land-surface slope with 1 being
the most sensitive and 5 being the least sensitive.  An additional
attribute, hydrologic setting, represents areas with common hydrologic
characteristics.  These 11 hydrologic settings are represented by a
letter code symbol.  The process step section below describes the
attributes in more detail and how the attributes were developed from
source data. The source data includes digital maps that characterize
the geology, precipitation distribution, and water levels, which have
been compiled at 1:100,000 scale and published in 1999 and 2000
as part of the Black Hills Hydrology Study. USGS Digital elevation
models were used to describe land-surface altitudes.  This data set
has been archived at the USGS Water Resources National Spatial Data
Information Node.
			</abstract>
			<purpose>
This data set was created to describe the sensitivity of ground
water to contamination in Lawrence County, SD. An additional
mechanism of transport of potential contaminants is streamflow loss
(infiltration). Mechanisms of potential contamination considered were
limited to those that can occur near the land surface and did not
include deep subsurface injection.  Ground water, for the purposes of
this data set, refers to the water in the uppermost saturated rocks
and sediments that can be yielded in usable quantities to a well or
spring.  Transport of a potential contaminant was assumed to occur
from infiltration of precipitation from the land surface to the
uppermost saturated rocks.  Runoff from precipitation on drainage
basins upstream from streamflow-loss zones affects the sensitivity of
map areas containing the losing stream.  Therefore, two additional
digital data sets delineating and describing streamflow loss zones
and drainage basins above them should be conjunctively considered
when evaluating sensitivity to contamination (see cross-reference
to obtain these digital data sets).  These data sets provide
some information about the upstream drainage basins that can be
compared but no attempt was made to provide a relative ranking of
sensitivity based on this information. The intended use of the
sensitivity data sets is as a screening tool used in conjunction with
other information and analysis.  Some relative comparisons can be made
between factors that influence sensitivity of ground-water to
contamination.  The map is not designed to replace the need for
site-specific investigations or to be the sole criterion in making
land-use decisions.
			</purpose>
			<supplinf>
This electronic report was subjected to the same review
standard that applies to all U.S. Geological Survey
reports. Reviewers were asked to check the topological
consistency, tolerances, attribute frequencies and
statistics, projection, and geographic extent. The reviewers
checked the metadata and a_readme.1st files for completeness and
accuracy.

Any use of trade, product, or firm names is for descriptive purposes
only and does not imply endorsement by the
U.S. Government.

Although this Federal Geographic Data Committee-compliant metadata
file is intended to document the data set in nonproprietary form,
as well as in ARC/INFO format, this metadata file may include some
ARC/INFO-specific terminology.

Other_References_Cited:
Aller, L., Bennett, T., Lehr, J.H., Petty, R.J., and Hackett, G.,
1987, DRASTIC:  A standardized system for evaluating ground water
pollution potential using hydrogeologic settings:  U.S. Environmental
Protection Agency, EPA/600/2-87/035, 455 p.

Strobel, M.L., Jarrell, G.J., Sawyer, J.F., Schleicher, J.R., and
Fahrenbach, M.D., 1999, Distribution of hydrogeologic units in the
Black Hills area, South Dakota:  U.S. Geological Survey Hydrologic
Investigations Atlas HA-743, 3 sheets, scale 1:100,000.
			</supplinf>
		</descript>
		<timeperd>
			<timeinfo>
				<sngdate>
					<caldate>19990609</caldate>
				</sngdate>
			</timeinfo>
			<current>
The sensitivity polygons are as current as the maps from which the
information was derived. The DEM's were compiled from a range of
dates specific to each 1:24,000 quadrangle.  Precipitation data and
the hydrogeologic units map are from 1999 interpretations for the
Black Hills Hydrology study.
			</current>
		</timeperd>
		<status>
			<progress>Complete</progress>
			<update>None Planned</update>
		</status>
		<spdom>
			<bounding>
				<westbc>-104.06234134</westbc>
				<eastbc>-103.43977512</eastbc>
				<northbc>44.60926227</northbc>
				<southbc>44.13453073</southbc>
			</bounding>
		</spdom>
		<keywords>
			<theme>
				<themekt>None</themekt>
				<themekey>Contamination</themekey>
				<themekey>Ground water</themekey>
				<themekey>Aquifer sensitivity</themekey>
				<themekey>Black Hills, aquifer vulnerability</themekey>
				<themekey>inlandWaters</themekey>
			</theme>
			<place>
				<placekt>None</placekt>
				<placekey>Lawrence County</placekey>
				<placekey>Black Hills</placekey>
				<placekey>South Dakota</placekey>
			</place>
		</keywords>
		<accconst>None</accconst>
		<useconst>
A limitation that needs to be considered when using the data
set is scale. The scale of the map is 1:100,000; therefore,
the hydrogeologic information includes numerous generalizations.
Modifying or overlaying the map at a scale that is more detailed
than the original map may be extremely misleading.
		</useconst>
		<ptcontac>
			<cntinfo>
				<cntperp>
					<cntper>Larry D. Putnam</cntper>
					<cntorg>U.S. Geological Survey</cntorg>
				</cntperp>
				<cntpos>Hydrologist</cntpos>
				<cntaddr>
					<addrtype>Mailing and physical address</addrtype>
					<address>1608 Mt. View Rd</address>
					<city>Rapid City</city>
					<state>South Dakota</state>
					<postal>57702</postal>
					<country>USA</country>
				</cntaddr>
				<cntvoice>1-888-275-8747</cntvoice>
				<cntfax>(605) 355-4523</cntfax>
				<cntemail>(ldputnam@usgs.gov)</cntemail>
			</cntinfo>
		</ptcontac>
		<datacred>
Compilation of this data set and the associated metadata was
funded in cooperation with Lawrence County, SD and the City
of Spearfish, SD.
		</datacred>
		<native>
SunOS, 5.6, sun4u UNIX
ARC/INFO version 8.0.1
		</native>
		<crossref>
			<citeinfo>
				<origin>Larry D. Putnam</origin>
				<pubdate>2000</pubdate>
				<title>
Drainage Areas Upstream from Potential Streamflow-loss Zones
in Lawrence County, SD
				</title>
				<geoform>Digital map</geoform>
				<serinfo>
					<sername>NA</sername>
					<issue>NA</issue>
				</serinfo>
				<pubinfo>
					<pubplace>Rapid City, South Dakota, USA</pubplace>
					<publish>U.S. Geological Survey</publish>
				</pubinfo>
				<onlink>http://water.usgs.gov/lookup/getspatial?sd_lcsens_da</onlink>
			</citeinfo>
		</crossref>
		<crossref>
			<citeinfo>
				<origin>Larry D. Putnam</origin>
				<pubdate>2000</pubdate>
				<title>Potential Streamflow-loss Zones in Lawrence County</title>
				<geoform>Digital map</geoform>
				<serinfo>
					<sername>NA</sername>
					<issue>NA</issue>
				</serinfo>
				<pubinfo>
					<pubplace>Rapid City, South Dakota, USA</pubplace>
					<publish>U.S. Geological Survey</publish>
				</pubinfo>
				<onlink>http://water.usgs.gov/lookup/getspatial?sd_lcsens_lz</onlink>
			</citeinfo>
		</crossref>
	</idinfo>
	<dataqual>
		<attracc>
			<attraccr>
Multiple visual checks were done to verify that the attribute
data was coincident with the original source map.
			</attraccr>
		</attracc>
		<logic>
Polygon topology present-polygon have
a label and all polygons are closed.
		</logic>
		<complete>
The digital map includes all sensitivity polygons and associated sensitivity-
unit codes as shown on PLATE 1 in USGS WRIR 00-4103
		</complete>
		<posacc>
			<horizpa>
				<horizpar>
The physical accuracy of the source
maps is unknown.
				</horizpar>
			</horizpa>
		</posacc>
		<lineage>
			<srcinfo>
				<srccite>
					<citeinfo>
						<origin>Greg Jarrell, John Schleicher</origin>
						<pubdate>2000</pubdate>
						<title>Hydrogeologic Units in the Black Hills area, South Dakota</title>
						<geoform>Digital map</geoform>
						<serinfo>
							<sername>Open-File Report</sername>
							<issue>USGS OFR 00-471</issue>
						</serinfo>
						<pubinfo>
							<pubplace>Rapid City, South Dakota</pubplace>
							<publish>U.S. Geological Survey</publish>
						</pubinfo>
						<onlink>http://water.usgs.gov/lookup/getspatial?ofr00471_hydrogeo</onlink>
					</citeinfo>
				</srccite>
				<srcscale>100000</srcscale>
				<typesrc>digital</typesrc>
				<srctime>
					<timeinfo>
						<sngdate>
							<caldate>1999</caldate>
						</sngdate>
					</timeinfo>
					<srccurr>
The ninteen references used to create this map range in date
from 1909 to 1998. Some field checking was done in selected
areas where less detailed source maps were available.
					</srccurr>
				</srctime>
				<srccitea>
None
This map was the primary source for determining the
spatial distribution of hydrogeologic units.
				</srccitea>
				<srccontr>This source provided the outlines of geologic formation outcrops.</srccontr>
			</srcinfo>
			<srcinfo>
				<srccite>
					<citeinfo>
						<origin>U.S. Geological Survey</origin>
						<pubdate>19790701</pubdate>
						<title>7.5 minute Digital Elevation Models</title>
						<geoform>Digital map</geoform>
						<pubinfo>
							<pubplace>Reston, VA, USA</pubplace>
							<publish>U.S. Geological Survey</publish>
						</pubinfo>
						<onlink>http://edc.usgs.gov.nsdi/html/dem75/dem75#section7</onlink>
					</citeinfo>
				</srccite>
				<typesrc>digital</typesrc>
				<srctime>
					<timeinfo>
						<rngdates>
							<begdate>19790701</begdate>
							<enddate>Present</enddate>
						</rngdates>
					</timeinfo>
					<srccurr>Range of dates of source material for DEM production</srccurr>
				</srctime>
				<srccitea>DEM</srccitea>
				<srccontr>
The source provided the spatial distribution of land surface
elevation for determining depth-to-water and land-surface-slope
categories.
				</srccontr>
			</srcinfo>
			<srcinfo>
				<srccite>
					<citeinfo>
						<origin>Joel Galloway, Ghaith Hamade, Gregory Jarrell</origin>
						<pubdate>2000</pubdate>
						<title>
Potentiometric surface contours for the Inyan Kara
aquifer, Black Hills, South Dakota
						</title>
						<geoform>Digital map</geoform>
						<serinfo>
							<sername>Open-File Report</sername>
							<issue>USGS OFR 00-471</issue>
						</serinfo>
						<pubinfo>
							<pubplace>Rapid City, South Dakota, USA</pubplace>
							<publish>U.S. Geological Survey</publish>
						</pubinfo>
						<onlink>http://water.usgs.gov/lookup/getspatial?ofr00471_inkrpcon</onlink>
					</citeinfo>
				</srccite>
				<srcscale>100000</srcscale>
				<typesrc>digital</typesrc>
				<srctime>
					<timeinfo>
						<sngdate>
							<caldate>19980730</caldate>
						</sngdate>
					</timeinfo>
					<srccurr>
The contours were drawn with information on elevation,
geologic outcrops, geologic structure, and water levels from
wells drilled as of 1998.
					</srccurr>
				</srctime>
				<srccitea>None</srccitea>
				<srccontr>
This map was used to calculate the depth to water for the Inyan
Kara aquifer.
				</srccontr>
			</srcinfo>
			<procstep>
				<procdesc>
This product is the digital version of the sensitivity polygons
on Plate 1 in USGS WRIR 00-4103, which documents the process used
in creating the map in detail.  The sensitivity polygons were
derived by sequential overlaying and intersecting five digital-map
coverages that represented hydrologic setting, hydrogeologic unit
(aquifer media, unsaturated media, and hydraulic conductivity),
recharge rate, depth to water, land-surface slope.  The polygons
produced from the overlaying layers retained a code from each map
layer that was unique to the polygon. The hydrologic setting is
represented by a numeric attribute. The letter code, hydrogeologic
unit, represents evaluation of (1) aquifer media, (2) unsaturated media
(3) hydraulic conductivity for sensitivity comparisons.  These
factors were grouped because they are all related to the rock and
sediments.  Forty-five unique hydrogeologic units where characterized
and ranked in descending order and sorted on the sensitivity rating
for unsaturated media, then aquifer media, and then hydraulic
conductivity.  The codes begin with an uppercase "A" and continue
through lower case "s."  When the first 26 uppercase letters were
used, the codes were continued with lower case letters. The first
digit in the sensitivity-unit code represents the recharge rate
with group 1 the most sensitive and group 4 the least sensitive.
The second digit in the sensitivity-unit code represents the depth
to water.  The depth-to-water digit includes two comparison groups,
quantitative groups and qualitative groups.  The quantitative groups,
which include areas where estimates of depth to water were available,
were ranked with group 1 the most sensitive and group 3 the least
sensitive.  The two qualitative groups were areas with highly variable
depths to water.  The stream valleys in the mountainous areas (group 4)
were assumed to have shallower depths to water than adjacent areas
(group 5) with highly variable depths to water.  Although the depth to
water is highly variable, the delineation provides a basis for some
relative comparisons of groups 4 and 5 with 5 being the least sensitive.
The third digit in the sensitivity-unit code represents the land-surface
slope, which consists of five groups, with group 1 the most sensitive
and group 5 the least sensitive. Below is a summary of the main process
steps used to create the sensitivity polygons shown on USGS WRIR 00-4103
Plate 1.

STEP 1: The first step to delineate sensitivity polygons was to
subdivide the study area into a geographic framework of hydrologic
settings with generally similar hydrogeologic characteristics.
Eleven settings were delineated in Lawrence County based on
topography, precipitation patterns, and the digital hydrogeologic
units map for the Black Hills.  The hydrologic units map was used
as the physiographic base.

STEP 2:  Because of the significant differences in sensitivity
characteristics of the geologic formations, the hydrogeologic-unit
coverage, (collectively represents aquifer media, unsaturated media,
and hydraulic conductivity) was selected as the next descriptive map
layer. This layer was derived from the hydrogeologic units map for
the Black Hills, but represents a new coverage.
Forty-five hydrogeologic units were delineated based on the
intersection of the hydrologic settings layer and outlines of
geologic formations with related assessments of aquifer media,
unsaturated media, and hydraulic conductivity.  Each hydrogeologic
unit was identified by an alphabetic character beginning with
capital letters and continuing with lowercase letters.  The
hydrogeologic units were sorted in descending order (A-Z, the a-s)
based on the relative sensitivity rating from most sensitive to
least sensitive.

STEP 3: A map delineating 4 categories of recharge-rate with 1
most sensitive and 4 the least sensitive was overlaid and
intersected with the previous map.  The recharge rate map was
created by developing grided data that estimated recharge rate as a
percent of precipitation for each hydrogeologic unit and multiplying
this grid by a grid of average precipitation interpolated from
precipitation gaging stations.

STEP 4: A map delineating 5 depth-to-water categories was overlaid
and intersected with the previous map. Smaller depths to water were
considered more sensitive. Three quantitative categories (1-3) and
two qualitative categories (4,5) were used to describe depth to
water. Groups 1 through 3 represented areas where data was available
to estimate depth-to-water categories with 1 most sensitive and 3
least sensitive. Areas with steeply dipping strata of fractured
rocks were not categorized for depth to water because of the large
variations in topography and water levels. In areas where data was
insufficient to characterize depth to water, the shallower depth to
water generally exists in stream valleys; therefore, areas with
land-surface elevations less than 50 ft above streambed elevations
were delineated as group 4 to make relative comparisons with areas
greater than 50 ft above streambed elevations, which were group 5.

STEP 5:  A map representing land-surface slope categories
was overlaid and intersected with the previous map to create the
final map. The land-surface slope categories were calculated
from 30-meter resolution digital elevation models (DEM). Flatter
slopes were considered more sensitive because a potential
contaminant would be more likely to runoff before infiltrating to
the water table. Five categories were delineated with 1 most
sensitive and 5 least sensitive. The intersecting of these map
layers resulted in 956 polygons with associated sensitivity-unit
codes.
				</procdesc>
				<procdate>1999</procdate>
			</procstep>
			<procstep>
				<procdesc>
First draft of metadata created by ldputnam using
FGDCMETA.AML ver. 1.33 07/15/99 on ARC/INFO data set
/home/project/ldp/projects/lawco.vuln/finalcovs/sens_pol
				</procdesc>
				<procdate>20010122</procdate>
			</procstep>
		</lineage>
	</dataqual>
	<spdoinfo>
		<direct>Vector</direct>
		<ptvctinf>
			<sdtsterm>
				<sdtstype>Point</sdtstype>
				<ptvctcnt>956</ptvctcnt>
			</sdtsterm>
			<sdtsterm>
				<sdtstype>String</sdtstype>
				<ptvctcnt>2868</ptvctcnt>
			</sdtsterm>
			<sdtsterm>
				<sdtstype>GT-polygon composed of chains</sdtstype>
				<ptvctcnt>957</ptvctcnt>
			</sdtsterm>
			<sdtsterm>
				<sdtstype>Point</sdtstype>
				<ptvctcnt>4</ptvctcnt>
			</sdtsterm>
		</ptvctinf>
	</spdoinfo>
	<spref>
		<horizsys>
			<planar>
				<mapproj>
					<mapprojn>Transverse Mercator</mapprojn>
					<transmer>
						<sfctrmer>0.999600</sfctrmer>
						<longcm>-105.000000</longcm>
						<latprjo></latprjo>
						<feast>500000.000000</feast>
						<fnorth>0.000000</fnorth>
					</transmer>
				</mapproj>
				<planci>
					<plance>coordinate pair</plance>
					<coordrep>
						<absres>0.985814511776</absres>
						<ordres>0.985814511776</ordres>
					</coordrep>
					<plandu>Meters</plandu>
				</planci>
			</planar>
			<geodetic>
				<horizdn>North American Datum of 1927</horizdn>
				<ellips>Clarke 1866</ellips>
				<semiaxis>6378206.4</semiaxis>
				<denflat>294.98</denflat>
			</geodetic>
		</horizsys>
	</spref>
	<eainfo>
		<detailed>
			<enttyp>
				<enttypl>sd_lcsens_pol.aat</enttypl>
				<enttypd></enttypd>
				<enttypds></enttypds>
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						<edomvd></edomvd>
						<edomvds></edomvds>
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				<attrlabl>$FROMNODE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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			<attr>
				<attrlabl>$TONODE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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			<attr>
				<attrlabl>$LEFTPOLYGON</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
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						<edomv></edomv>
						<edomvd></edomvd>
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			<attr>
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				<attrdefs></attrdefs>
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						<edomv></edomv>
						<edomvd></edomvd>
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		</detailed>
		<detailed>
			<enttyp>
				<enttypl>sd_lcsens_pol.pat</enttypl>
				<enttypd></enttypd>
				<enttypds></enttypds>
			</enttyp>
			<attr>
				<attrlabl>FID</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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			<attr>
				<attrlabl>SHAPE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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			<attr>
				<attrlabl>AREA</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
					</edom>
				</attrdomv>
			</attr>
			<attr>
				<attrlabl>PERIMETER</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
					</edom>
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			</attr>
			<attr>
				<attrlabl>SD_LCSENS_POL#</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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				</attrdomv>
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			<attr>
				<attrlabl>SD_LCSENS_POL-ID</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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				</attrdomv>
			</attr>
			<attr>
				<attrlabl>SETTING</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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			</attr>
			<attr>
				<attrlabl>HGU-CODE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
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			<attr>
				<attrlabl>RECH-CODE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
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			</attr>
			<attr>
				<attrlabl>DW-CODE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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			<attr>
				<attrlabl>SLP-CODE</attrlabl>
				<attrdef></attrdef>
				<attrdefs></attrdefs>
				<attrdomv>
					<edom>
						<edomv></edomv>
						<edomvd></edomvd>
						<edomvds></edomvds>
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		</detailed>
		<overview>
			<eaover>
COLUMN   ITEM NAME        WIDTH OUTPUT  TYPE N.DEC  ALTERNATE NAME
1     AREA                   4    12     F      3
5     PERIMETER              4    12     F      3
9     SD_LCSENS_POL#         4     5     B      -
13    SD_LCSENS_POL-ID       4     5     B      -
17    SETTING                5     5     C      -
22    HGU-CODE               2     2     C      -
24    RECH-CODE              1     1     I      -
25    DW-CODE                1     1     I      -
26    SLP-CODE               1     1     I      -

AREA -Area of polygon in square meters
PERIMETER -Perimeter of polygon in meters
SD_LCSENS_POL# -Internal feature number
SD_LCSENS_POL-ID -Assigned feature number
SETTING -Assigned symbol representing hydrogeologic unit
HGU-CODE -Assigned number for hydrogeologic unit letter
in sensitivity-unit code
RECH-CODE -Assigned number for recharge-rate digit in
sensitivity-unit code
DW-CODE -Assigned number for depth to water digit in
sensitivity-unit code
SLP-CODE -Assigned number for slope digit in sensitivity-unit
code

List of hydrologic setting symbols,
name, and description for attribute SETTING

Ms-e Mountain Slopes-East

This setting, located in the southeastern and south-central part
of the study area, is characterized by steep slopes, thin soil cover,
and fractured bedrock consisting mostly of igneous and metamorphic
rocks.  Well yields typically are limited, although in local areas
the hydraulic conductivity could be high due to fracturing.  Thicker
weathered zones may develop locally particularly on talus slopes with
perched water common.  The topographic trend of these slopes is to
the east in the rain shadow of the mountains, and limited rainfall is
derived from moisture-laden prevailing westerly winds. Because of the
orographic effect of the Black Hills, the northern part of this
setting receives more rainfall than is typical for this setting.
Ground-water levels are extremely variable.

Ms-n Mountain Slopes-North

This setting, located on the northern slope of the uplift, is similar
to Mountain Slopes-East except precipitation generally exceeds that
which falls on eastern slopes.  Recharge remains relatively low,
however, because of the steep slopes and low primary porosity of the
rock.  In this particular setting, increased fracturing may occur in
areas along the flanks of igneous intrusions.

Amv-e Alluvial Mountain Valleys-East

This setting, located in east sloping valleys within the mountain
slopes-east setting, is characterized by thin alluvium and boulders
derived from the surrounding steep slopes.  Soil cover generally is
gravel sized.  Ground water may be obtained from the alluvial
deposits and also from the fractures in the underlying bedrock,
which are generally in direct hydraulic connection with the alluvium.
This type of setting may be expected along most of the streams within
the Mountain Slopes-East setting; however, some contiguous mappable
areas may be less than 100 acres and consequently may not be shown on
the map.

Amv-n Alluvial Mountain Valleys-North

This setting, located within the Mountain Slopes-North setting, is
similar to the Alluvial Mountain Valleys-East setting.  Ground-water
levels are typically shallower because of higher amounts of
precipitation and subsequently greater recharge.  This type of
setting may be expected along most of the streams within the mountain
slopes-north setting; however, some contiguous mappable areas may be
less than 100 acres in many areas and consequently may not be shown
on the map.

Id Igneous Domes

This setting, located across the central part of the study area, is
characterized by igneous intrusive rocks surrounded by dipping
sedimentary rocks.  Folding and faulting of the sedimentary rocks
along the flanks of the domes may increase the permeability and the
recharge rate of these units.  Well yields are extremely variable
depending on the degree of folding and faulting and the type of rock.
Where few fractures exist in the igneous domes, well yields are very
low or non-existent; however, well yields typically are greater along
the fractured areas on the flanks of the domes.  Sedimentary rock
outcrops, hydraulically connected to the confined regional aquifers,
could have relatively large recharge rates because of increased
fracturing and relatively large precipitation amounts.

Lp Limestone Plateau

This setting, located in the southwestern part of the study area,
includes most of the area referred to locally as the "Limestone
Plateau."  This setting has more relief than the moderate and
variable topographic relief described in the "Solution Limestone
setting" in DRASTIC (Aller and others, 1984). The limestone is
characterized by a network of solution openings where the
limestone has been partially dissolved along bedding planes and
fractures.  Soil usually is thin or absent, but where present
commonly is a clayey loam.  Recharge usually is high because
infiltration of precipitation occurs easily through the fractures
and solution openings.  Return of recharge into surface water
courses can be high.  Water levels typically are moderately deep
except near surface discharge points.

Mf Mountain Flanks

This setting, located on the mountain flanks along the western,
north-central, and eastern parts of the study area, is characterized
by moderately dipping, fractured, consolidated sedimentary rocks.
Soil usually is thicker than on mountain slopes.  Ground water is
obtained from the permeable sedimentary rocks or from fractures in
the sedimentary rocks.  The recharge rate is higher in the western
and north-central parts because of greater precipitation.  The
mountain flanks serve as recharge areas for aquifers that are
confined in adjacent areas.

Amv Alluvial Mountain Valleys

This setting, located in narrow valleys within the igneous domes
and mountain flanks setting, is characterized by thin alluvium
and boulders that overlies fractured bedrock of sedimentary or
igneous intrusive origin.  Surficial deposits have typically
weathered to a sandy loam.  Ground water is obtained from sand
and gravel layers, which commonly are in direct hydraulic connection
to underlying bedrock. This type of setting may be expected along
most of the streams within the igneous domes and mountain flanks
settings; however, some contiguous mappable areas may be less than
100 acres in many areas and consequently may not be shown on the
map.

Sls Alternating Sandstone, Limestone and Shale-Thin Soil

This setting, located in the northern part of the study area, is
characterized by low to moderate topographic relief.  Relatively
thin loamy soils overlie horizontal or slightly dipping alternating
layers of fractured, consolidated sedimentary rocks.  Ground water
primarily is obtained from sandstone layers or fractures along
bedding planes or vertical fractures.  Recharge generally is
moderate to low.  Shale or clayey layers often form confining
layers and where sufficient relief is present, perched ground-water
zones of local importance often are developed.

Usd Unconsolidated or Semi-Consolidated Deposits

This setting is characterized by moderately low topographic relief
and interbedded deposits that consist of layers of clay, silt, and
sand.  Although soils are typically loamy or sandy, recharge is
limited because of moderate precipitation and high
evapotranspiration.  Ground-water levels typically are less than
50 feet.

Ra River Alluvium without Overbank Deposits

This setting is characterized by low topographic relief and deposits
of alluvium along stream valleys.  Ground-water levels typically
are shallow.  Infiltration of precipitation is rapid but limited by
the amount of precipitation.  Interaction between the stream and the
ground-water system is significant.

List of hydrogeologic unit code, hydrologic setting,
geologic unit, and comments for attribute HGU_CODE

A  Igneous Domes  Madison Limestone-Englewood Formation

This part of the Madison Limestone outcrop is located across the
central part of the study area near intrusive rocks.  Inventoried
well yields in the regional Madison aquifer are highly variable
with the largest group ranging from 10 to 200 gal/min and a
significant number of wells between 400 and 1,750 gal/min.
Permeability is mainly from enhanced solution openings, which
occur predominantly in the upper 200 ft of the formation,
and fractures.  Additional fracturing is possible due to igneous
intrusive activity.  Hydraulic conductivity determined from
aquifer tests of wells with larger yields are in the range of
200 ft/d.  Rapid movement of potential contaminants with
little attenuation through solution openings or fractures in the
aquifer media and unsaturated media is likely.  Little well
information is available for the Englewood Formation, and
hydrogeologic characteristics were assumed to be similar to the
overlying lower Madison Limestone.

B  Limestone Plateau  Madison Limestone-Englewood Formation

This part of the Madison Limestone outcrop, located within the
Spearfish Creek drainage basin, includes a large part of Limestone
Plateau setting.  Inventoried well yields within the unconfined
outcrop area are less than 20 gal/min.  Permeability is from
enhanced solution openings, which occur predominantly in the upper
200 ft of the formation and fractures.  Ground-water flow is
towards springs discharging to Spearfish Creek and Rapid Creek,
and to the regional Madison aquifer.  Rapid movement of potential
contaminants with little attenuation through solution openings or
fractures in the aquifer media and unsaturated media is likely.

C Mountain Flanks  Madison Limestone-Englewood Formation

This part of the Madison Limestone outcrop is located in the
southeastern and southwestern part of the study area, near
Spearfish Creek, and a small area in the east-central part of the
study area.  Ground-water flow generally is radially outward from
the central part of the Black Hills.  Sensitivity characteristics
are similar to unit A without the additional fracturing due to
igneous intrusive activity.

D  Limestone Plateau  Madison Limestone-Englewood Formation

This part of the Madison Limestone outcrop is located east of
Spearfish Creek.  The yields of the few inventoried wells located
within the hydrogeologic unit range from 2 to 200 gal/min.
Ground-water flow directions are related to topography and surface
drainage patterns.  The area is not directly connected to the
regional Madison aquifer but does contribute base flow to
headwaters of Spearfish, Whitewood, Elk, and Rapid Creeks.
Hydraulic conductivity probably is less than determined for higher
producing wells in the regional aquifer due to limited saturation
and erosion of the more permeable upper parts of the formation.
Movement of potential contaminants with little attenuation through
solution openings or fractures in the aquifer media and unsaturated
media is possible.

E  Mountain Flanks  Minnekahta Limestone

This part of the Minnekahta Limestone outcrop is located in an
east-west direction across the north-central part of the study
area.  Most inventoried well yields range from 2 to 200 gal/min
with some well yields as much as 500 gal/min.  Permeability
primarily is from fractures with some solution openings.
Estimates of hydraulic conductivity from production well data
range from less than 10 to 60 ft/d.  Vertical movement in the
unsaturated zone is rapid with little attenuation of potential
contaminants.

F  Alternating Sandstone, Limestone, and Shale  Minnekahta Limestone

This part of the Minnekahta Limestone outcrop is exposed in a
narrow band around Elkhorn Peak.

G  Alluvial Mountain Valleys-East  Alluvium

This alluvium is located in the southern part of the study area
within mountain slopes-east.  Particle size probably is larger
than most alluvium because of high stream velocities.  Similar
alluvium is likely along all streams in this setting although the
area may not be shown due to size and map-scale limitations.
Saturation is variable depending on streamflow conditions.

H  Alluvial Mountain Valleys-North  Alluvium

This alluvium is located in the central part of the study area
within Mountain Slopes-North.  Sensitivity characteristics are
similar to unit G.

I  Alluvial Mountain Valleys  Alluvium

This alluvium is located around the perimeter of the Black Hills
uplift in the southern and central part of the study area within
the Igneous Domes and Mountain Flanks settings.  Similar alluvium
is likely along streams in this setting although the area may not
be shown due to size and map-scale limitations.  Saturation is
variable depending on streamflow conditions.

J  River Alluvium without Overbank Deposits  Alluvium

This alluvium is located along streams in the northern part of
the study area with gentler topographic relief than in the
mountain settings.  Inventoried well yields range from 10 to 60
gal/min.   Saturation is more consistent along the perennial
streams.

K  Unconsolidated and Semi-Consolidated Deposits  Gravel deposits

These deposits are local aquifers where saturated and generally
consist of terraces and former flood plains located adjacent to
recent alluvial deposits.  Inventoried well yields range from 10
to 100 gal/min.   Saturation of the unit varies with the altitude
of the unit in relation to adjacent alluvium and hydrologic
conditions.

L  Mountain Flanks  Minnelusa Formation

This part of the Minnelusa Formation outcrop is located east to
west across the central part of the study area and north to south
along the southwestern part of the study area.  Inventoried well
yields are highly variable with the largest group ranging from 10
to 200 gal/min, a considerable number between 200 and 700 gal/min,
and a few wells as much as 1,700 gal/min.  Permeability is from
the primary porosity of sandstone layers.  Secondary porosity is
from fractures and dissolved anhydrite collapse features.  The
lower part of the formation, with interbedded shales, generally
is considered a confining layer with highly variable leakage to
and from the Madison Limestone due to fractures and brecciation.
Hydraulic conductivity is variable with values of about 50 ft/d
determined from aquifer tests at public supply wells.  Some
attenuation of potential contaminants is possible with movement
through sandstone; however, considerable variability is probable
due to fractures and collapse features.

M  Alternating Sandstone, Limestone, and Shale  Minnelusa Formation

This part of the Minnelusa Formation outcrop is located in the
northeastern part of the study area.  Erosion of the more
permeable upper parts of the formation probably decreases the
hydraulic conductivity and vertical movement of a potential
contaminant in the unsaturated zone compared to unit L.

N  Igneous Domes  Deadwood  Formation

This part of the Deadwood Formation outcrop is located east to
west across the central part of the study area.  Inventoried well
yields are highly variable with the largest group less than
50 gal/min, several between 50 and 300 gal/min, and a few wells
as much as 1,100 gal/min.  Wells generally are located near to or
on the outcrop.  Permeability is from the primary porosity of
sandstone layers and secondary porosity from fractures.  This
part of the outcrop is near intrusive igneous bodies and often
includes sills, which increase the fracturing.  The ground-water
flow patterns are very complex because of the intrusive bodies
and include a mixture of local and regional ground-water flow
systems.  Movements of potential contaminants could be highly
variable because of the complex fracturing patterns.

O  Limestone Plateau  Deadwood  Formation

This part of the Deadwood Formation outcrop is located along
Spearfish Creek and the headwaters of Elk, Boxelder, and Rapid
Creeks.  Ground water could be close to the surface in parts of
this area because of the interaction between the streams and the
Deadwood aquifer.  Many of the smaller tributaries flowing across
this area have perennial flow because of springs discharging from
the Madison or Deadwood aquifers.

P  Igneous Domes  Minnelusa  Formation

These small areas of Minnelusa Formation outcrop, located on the
eastern and western edges of the central part of the study area,
are isolated from the regional Minnelusa aquifer.  Erosion of the
more permeable upper part of the formation probably decreases
hydraulic conductivity and the movement of potential contaminants
in the unsaturated zone.  No inventoried well information is
available for the unit and saturation could be limited because of
discharge to the surrounding Madison aquifer, which has a lower
altitude.

Q  Limestone Plateau  Minnelusa Formation

This small area of Minnelusa Formation outcrop, located within the
Limestone Plateau, is isolated from the regional Minnelusa aquifer.
Erosion of the more permeable upper part of the formation probably
decreases hydraulic conductivity and the sensitivity
characteristics of the unsaturated zone.  No inventoried well
information is available for the unit and saturation could be
limited because of discharge to the surrounding Madison aquifer,
which has a lower altitude.

R  Mountain Flanks  Deadwood  Formation

This part of the Deadwood Formation outcrop is located in the
southeastern part of the study area, and a small area is located
near Spearfish Creek.  Permeability is from the primary porosity
of sandstone layers and secondary porosity from fractures.  The
general direction of ground-water flow in the southeastern area
is to the east, and average precipitation is less than on the
other Deadwood Formation outcrops.

S  Mountain Slopes-East  Deadwood  Formation

This part of the Deadwood Formation outcrop is located within the
Precambrian rocks in the southern part of the study area.
Permeability is from the primary porosity of sandstone layers and
secondary porosity from fractures.  Some of the areas may be
isolated from the regional Deadwood aquifer with ground-water
flow patterns determined by local topography and hydraulic
connection to underlying rocks.

T  Mountain Slopes-East  Igneous and metamorphic rocks

This hydrogeologic unit, located in the southeastern and south
central part of the study area is a local aquifer where saturated.
Wells are located on or very close to the outcrop.  Most
inventoried well yields range from 5 to 20 gal/min with some well
yields up to 60 gal/min.  The depth of wells generally are less
than 200 ft.  Permeability is from fracturing that decreases with
depth.  Ground-water flow patterns are complex and variable.

U Mountain Slopes-North  Igneous and metamorphic rocks

This hydrogeologic unit, located in the central part of the study
area, is a local aquifer where saturated.  Wells are located on or
very close to the outcrop.  Most inventoried well yields are less
than 20 gal/min with one reported yield of 60 gal/min.  This well
was in an area where numerous sills have penetrated the Precambrian
rocks.  Permeability is from fracturing that decreases with depth.
Ground-water flow patterns are complex and variable.

V  Mountain Flanks  Igneous and metamorphic rocks

This hydrogeologic unit, located in the southeastern part of the
study area and surrounded by the Deadwood Formation, is a local
aquifer where saturated.  An inventoried well yield was 5 gal/min.
Permeability is from fracturing that decreases with depth.
Ground-water flow patterns are complex and variable.

W  Mountain Slopes-East Colluvium

This hydrogeologic unit, located within the Precambrian rocks in
the southern part of the study area, could supply limited
quantities of water where saturated.   No information is available
to describe well yields or hydraulic conductivity.  Considerable
variation in sensitivity characteristics is likely depending on
the particle size and sorting of the deposits.

X  Igneous Domes Colluvium

This hydrogeologic unit, located on the slopes of igneous domes
in the western part of the study area, probably would have limited
saturation because of the land-surface slope.

Y  Mountain Flanks  Colluvium

This hydrogeologic unit, located in the east-central part of the
study area, could supply limited quantities of water where
saturated.  No information is available to describe well yields or
hydraulic conductivity.  Considerable variation in sensitivity
characteristics is likely depending on the particle size and
sorting of the deposits.

Z  Alternating Sandstone, Limestone, and Shale Inyan Kara Group:
Fall River Formation and Lakota Formation

The Inyan Kara Group outcrop is located in the northeastern part
of the study area.  Inventoried well yields in the Inyan Kara
aquifer mostly are less than 50 gal/min, with a few wells between
50 and 200 gal/min.  The majority of permeability is from the
primary porosity of the sandstone.

a Igneous Domes Tertiary intrusive igneous rocks

This hydrogeologic unit, located in the central part of the study
area, includes most of the centers of igneous activity in the
northern Black Hills in South Dakota.  Inventoried well yields
completed in intrusive rocks generally are less than 20 gal/min.
Well yields and hydraulic conductivity in the massive domes
probably would be low.  Larger well yields could be expected
where the outcrop is exposed as shallow sills intruding the
Deadwood Formation.  The lithology for several of the wells in
this area that are identified as Deadwood aquifer wells include
layers of intrusive rocks.  Ground-water flow patterns are complex
and variable.

b  Mountain Slopes-East  Tertiary intrusive igneous rocks

These two hydrogeologic units are located within the Precambrian
rocks in the south-central part of the study area.  No well
inventory information is available.

c  Mountain Slopes-North  Tertiary intrusive igneous rocks

This hydrogeologic unit is located within the Precambrian rocks
in the central part of the study area.  Larger well yields
generally are found adjacent to Precambrian rocks intruded with
shallowly placed sills, laccoliths, dikes, and plugs.
Ground-water flow patterns are complex and variable.

d  Igneous Domes  Whitewood Formation-Winnipeg Formation

This hydrogeologic unit is located in narrow bands adjacent to
Deadwood Formation outcrops and intrusive rocks in the east- to
west-central part of the study area.  The combined Whitewood
Formation and Winnipeg Formation is considered a semiconfining
unit in the study area.  No well inventory information is
available for the unit.  The overlying Madison aquifer or the
underlying Deadwood aquifer would be more likely sources of water.
The Whitewood Formation extends as far south as the intersection
of Spearfish Creek and Highway 85 with only few places where the
Winnipeg Formation extends farther south.  Permeability from
fractured limestone, dolomite, and siltstone could produce small
quantities of water.

e  Mountain Flanks Whitewood Formation-Winnipeg Formation

This hydrogeologic unit is located in the part of the Spearfish
Creek drainage basin just above the City of Spearfish.  The unit
is exposed along Spearfish Creek and its tributaries.

f  Limestone Plateau Whitewood Formation-Winnipeg Formation

This hydrogeologic unit is located in the upper part of the
Spearfish Creek drainage basin and the headwaters of Elk,
Boxelder, and Rapid Creek in the southern and central parts of
the study area.  The part of the unit exposed along Spearfish
Creek and its tributaries is a narrow band located part way up
the canyon wall above the Deadwood Formation outcrop, which is
exposed at the bottom of the canyon.  Most of these areas have
very steep slopes causing most precipitation that falls on the
outcrop to run off.

g  Mountain Flanks Whitewood Formation-Winnipeg Formation

This hydrogeologic unit, located in the southeastern corner of
the study area, dips to the east, and the general direction of
ground-water flow is to the east.

h  Alternating Sandstone, Limestone, and Shale  Morrison Formation,
Unkpapa Sandstone, Sundance Formation, Gypsum Spring Formation

This hydrogeologic unit, located in the northeastern part of the
study area, is a semiconfining unit with parts of the unit used
as an aquifer locally.  Reported well yields, primarily from wells
completed in the Sundance Formation, range from 5 to 70 gal/min.
Permeability mostly is from sandstone layers within the unit.

i  Mountain Slopes-East  White River Group

This part of the White River Group outcrop, located in the
east-central part of the study area, is a small area within
Precambrian rocks that has not been removed by erosion.  No well
inventory information is available.  Permeability mostly is from
sand and gravel lenses and fractured limestone.  Bentonite within
volcanic ash deposits could limit vertical movement of
contaminants.

j  Mountain Slopes-North  White River Group

This part of the White River Group outcrop, located in the
central part of the study area is a small area in a valley of
Precambrian rocks.

k  Igneous Domes  White River Group

This part of the White River Group outcrop is located in the
central part of the study area near igneous intrusive rocks.
No well inventory information is available.

l  Limestone Plateau  White River Group

This part of the White River Group outcrop, located in the
east-central part of the study area east of Spearfish Creek,
is a small area overlying Madison Limestone and Deadwood
Formation outcrops.

m  Mountain Flanks  White River Group

This part of the White River Group outcrop is located near
Madison Limestone and Minnelusa Formation outcrops along the
northern mountain flanks in the central part of the study area.

n  Alternating Sandstone, Limestone, and Shale  White River Group

This part of the White River Group outcrop is located near the
Inyan Kara Group outcrop in the northeastern part of the study
area.

o  Alternating Sandstone, Limestone, and Shale  Spearfish Formation

This hydrogeologic unit, located in an east-west direction across
the northern part of the study area, is a confining unit that
supplies water to several wells.  Most reported well yields are
less than 20 gal/min with a few between 20 and 100 gal/min and one
well yielding 300 gal/min.  Thickness ranges from 375-450 ft along
the eastern side of the Black Hills uplift to 700-800 ft on the
northwestern flank of the uplift.12  Permeability is from porous
lenses and secondary porosity associated with gypsum solution
openings.  Attenuation of potential contaminants by silts and
shale is probable.

p  Mountain Flanks Spearfish Formation

This hydrogeologic unit is isolated areas of the Spearfish
Formation that have not eroded away.  The part of the unit located
on the western side of the study area slopes to the northwest.
The part of the unit located on the east side of the study area
slopes to the northeast.  Limited saturation in these two areas is
likely.  No inventoried well information is available.

q  Alternating Sandstone, Limestone, and Shale  Belle Fourche Shale,
Mowry Shale, Newcastle Sandstone, Skull Creek Shale

This hydrogeologic unit, located in the northeastern corner of
the study area, is a confining unit.  The Newcastle Sandstone may
yield water to wells locally where saturated.  A single well in
the Belle Fourche Shale produced 20 gal/min.  Vertical movement of
potential contaminants is limited by shale and bentonite layers.

r  Mountain Flanks Opeche Shale

This hydrogeologic unit is located in narrow bands between the
Minnelusa Formation and Minnekahta Limestone across the
north-central part of the study area.  The Opeche Formation is a
confining unit that produces water to wells in isolated areas.
Most reported well yields range from 2 to 20 gal/min with a few
wells as much as 75 gal/min.  Permeability is from porous lenses,
solution features, and/or fractures.  Attenuation of potential
contaminants by silt and shale is probable.  Drainage from the
area could recharge the Minnekahta aquifer.

s Alternating Sandstone, Limestone, and Shale  Opeche Shale

This hydrogeologic unit is located in a narrow ring between the
Minnelusa Formation and Minnekahta Limestone around a peak in the
northeastern part of the study area near Polo Creek.  Drainage
from the area could recharge the Minnekahta aquifer.

List of Recharge-rate group, Recharge rate (inches/year)
and Sensitivity rank for attribute RECH-CODE

1      7 to &lt;10       Highest
2      4 to &lt;7
3      2 to &lt;4
4      0 to &lt;2        Lowest

List of depth-to water group, depth to water (feet),
and relative sensitivity rank for attribute DWA-CODE

1     0 to &lt;20 feet   Highest
2     20 to &lt;50 feet                      Compare group 1, 2, 3
3     50 or &gt;50       Lowest              (not to groups 4 and 5)

4     Highly variable (areas of fractured
rock in stream valleys)             Compare group 4 and 5
5     Highly variable (other areas)       (not groups 1, 2, and 3)

List of land-surface-slope group, land-surface slope
(percent) and sensitivity rank for attribute SLP-CODE

1     0 to &lt;2        Highest
2     2 to &lt;6
3     6 to &lt;12
4     12 to &lt;18
5     18 or &gt;18      Lowest
			</eaover>
			<eadetcit>none</eadetcit>
		</overview>
	</eainfo>
	<distinfo>
		<distrib>
			<cntinfo>
				<cntorgp>
					<cntorg>U.S. Geological Survey</cntorg>
				</cntorgp>
				<cntpos>Ask USGS - Water Webserver Team</cntpos>
				<cntaddr>
					<addrtype>mailing</addrtype>
					<address>445 National Center</address>
					<city>Reston</city>
					<state>VA</state>
					<postal>20192</postal>
				</cntaddr>
				<cntvoice>1-888-275-8747 (1-888-ASK-USGS)</cntvoice>
				<cntemail>http://answers.usgs.gov/cgi-bin/gsanswers?pemail=h2oteam&amp;subject=GIS+Dataset+sd_lcsens_pol</cntemail>
			</cntinfo>
		</distrib>
		<distliab>Although this data set has been used by the U.S. Geological
Survey, U.S. Department of the Interior, no warranty expressed or
implied is made by the U.S. Geological Survey as to the accuracy
of the data and related materials. The act of distribution shall not 
constitute any such warranty, and no responsibility is assumed by 
the U.S. Geological Survey in the use of this data, software, or 
related materials.

Any use of trade, product, or firm names is for descriptive
purposes only and does not imply endorsement by the U.S.
Government.</distliab>
		<stdorder>
			<digform>
				<digtinfo>
					<formname>Export</formname>
					<formcont>Full coverage</formcont>
					<filedec>zipped</filedec>
					<transize>1</transize>
				</digtinfo>
				<digtopt>
					<onlinopt>
						<computer>
							<networka>
								<networkr>http://water.usgs.gov/GIS/dsdl/sd_lcsens_pol.e00.gz</networkr>
							</networka>
						</computer>
					</onlinopt>
				</digtopt>
			</digform>
			<digform>
				<digtinfo>
					<formname>SDTS</formname>
					<formcont>Full coverage</formcont>
					<filedec>zipped</filedec>
					<transize>1</transize>
				</digtinfo>
				<digtopt>
					<onlinopt>
						<computer>
							<networka>
								<networkr>http://water.usgs.gov/GIS/dsdl/sd_lcsens_pol_sdts.tar.gz</networkr>
							</networka>
						</computer>
					</onlinopt>
				</digtopt>
			</digform>
			<digform>
				<digtinfo>
					<formname>Other</formname>
					<formcont>Full coverage</formcont>
					<filedec>zipped</filedec>
					<transize>1</transize>
				</digtinfo>
				<digtopt>
					<onlinopt>
						<computer>
							<networka>
								<networkr>http://water.usgs.gov/GIS/dsdl/sd_lcsens_pol_shape.tar.gz</networkr>
							</networka>
						</computer>
					</onlinopt>
				</digtopt>
			</digform>
			<fees>None. This dataset is provided by USGS as a public service.</fees>
		</stdorder>
	</distinfo>
	<metainfo>
		<metd>20041108</metd>
		<metc>
			<cntinfo>
				<cntorgp>
					<cntorg>U.S. Geological Survey</cntorg>
				</cntorgp>
				<cntpos>Ask USGS -- Water Webserver Team</cntpos>
				<cntaddr>
					<addrtype>mailing</addrtype>
					<address>445 National Center</address>
					<city>Reston</city>
					<state>VA</state>
					<postal>20192</postal>
				</cntaddr>
				<cntvoice>1-888-275-8747 (1-888-ASK-USGS)</cntvoice>
				<cntemail>http://answers.usgs.gov/cgi-bin/gsanswers?pemail=h2oteam&amp;subject=GIS+Dataset+sd_lcsens_pol</cntemail>
			</cntinfo>
		</metc>
		<metstdn>FGDC Content Standards for Digital Geospatial Metadata</metstdn>
		<metstdv>FGDC-STD-001-1998</metstdv>
	</metainfo>
</metadata>
