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pppppy -'. EPA Region 5 Records Ctr.
224228>.;.-.•v>-:- .v .--. ••&•'•
VOLUME 2 OF 2
PHASE 1 REPORT
SUPPLEMENTAL HYDROGEOLOGIC INVESTIGATIONLEMON LANE LANDFILL
Westinghouse Electric CorporationEnvironmental Systems and Services Division
Pittsburgh, PennsylvaniaI
November 1989BLASLAND & BOUCK ENGINEERS, P.C.
BLASLAND, BOUCK & LEEENGINEERS & GEOSCIENTISTS
VOLUME 2 OF 2
PHASE I REPORTSUPPLEMENTAL HYDROGEOLOGIC INVESTIGATION
LEMON LANE LANDFILL
WESTINGHOUSE ELECTRIC CORPORATIONENVIRONMENTAL SYSTEMS & SERVICES DIVISION
PITTSBURGH, PENNSYLVANIA
NOVEMBER 1989
BLASLAND & BOUCK ENGINEERS, P.C.6723 TOWPATH ROAD
SYRACUSE, NEW YORK 13214
VOLUME 1 OF 2
TABLE OF CONTENTS
SECTION I - INTRODUCTION
SECTION II - SUPPLEMENTAL HYDROGEOLOGIC INVESTIGATIONRESULTS
A. Introduct ionB. Task 1.1 Review of Previous Subsurface
and Analytical Invest igat ionsGeology and Hydrogeology ReviewKarst and Sur face Water Features ReviewSite ReconnaissanceContinuous Soil Test Bor ing/Rock CoringMonitoring Well Installation in BedrockGround-Water Elevation/Rainfall Measurement
1.8 Pre-Tracer Test Ground-Water andSurface Water Sampling
1.9 Ground-Water Tracer Tests
c.D.E.F.G.H.I.
TaskTaskTaskTaskTaskTaskTask
1.21.31.41.51.61.71.8
J. Task
SECTION III - INTERPRETATION OF INVESTIGATION RESULTS
A. Topography and GeomorphologyB. Overburden GeologyC. Bedrock GeologyD. Hydrology and Hydrogeology
Page
1
4
44
8101114162326
28
32
32323440
Table LL-1
Table LL-2
Table LL-3
Table LL-4
Table LL-5
Table LL-6
Table LL-7
Table LL-8
Table LL-9
Table LL-10
Table LL-11
VOLUME 1 OF 2
LIST OF TABLES
Chronology of Site Invest igat ions
PCB Analy t ica l Data for Soils and Sediments
PCB Analyt ica l Data for Ground Water and S u r f a c e Water
Ground-Water Monitor ing Well Detai ls
Ground-Water Elevations
Perennial and In termi t tent Springs Data
Ground-Water Monitor ing Well Detai ls, SupplementalHydrogeologic Invest igat ion
Hydraulic Conductivi ty Values f rom Packer Test ing
Hydraulic Conduct ivi ty Values f rom Slug Testing
Ground-Water Elevat ions, SupplementalHydrogeologic Invest igat ion
Duration of Continuous Water Elevationand Rainfall Measurement
Table LL-12 Marker Beds in the St. Louis Limestone
VOLUME 1 OF 2
LIST OF FIGURES
Figure LL-1 Regional Site Plan
Figure LL-2 Sampling Location
Figure LL-3 Regional Sampling Location Plan
Figure LL-4 Karst , Subsurface Solution, and Sur face Water Features
Figure LL-5 Monitoring Well Location Plan
Figure LL-6A Low Flow, Tracer Injection, Sampling, and Detection Locations
Figure LL-6B High Flow, Tracer Injection, Sampling, and Detection Locations
Figure LL-7A Geologic Cross Section A-A1
Figure LL-7B Geologic Cross Section B-B1
Figure LL-8 Bedrock St ructure Map
Figure LL-9 Fracture Trace/Lineament Map
Figure LL-10 PCB Water Quality Results
in
VOLUME 2 OF 2
LIST OF APPENulCES
Appendix LL-1
Appendix LL-2
Appendix LL-3
Appendix LL-4
Appendix LL-5
Appendix LL-6
Appendix LL-7
Appendix LL-8
Appendix LL-9A
Appendix LL-9B
Appendix LL-10
Appendix LL-11
Appendix LL-12
References
Powell Repor t , Geology and Hydrogeology ofLemon Lane Landfil l
Subsur face and Well Logs, 1982-1983
Subsur face and Well Logs. 1987
Packer Test Field Data and Detai ls
Slug Test Field Data
Caliper Logging Field Data
Gamma Ray Logging Field Data
Continuous Water Elevation Hydrographs
Storm-Event Hydrographs
Low Flow Tracer Test Reports, Hydroscience Assoc ia tes
Low Flow Tracer Tes t Memorandum, Blasland & BouckEngineers, P.C.
High Flow Tracer Test, Lemon Lane Landfil l, Bloomington,Indiana, Westinghouse Environmental and GeotechnicalServices, Inc.
iv
oX
APPENDIX LL-1
• '.'V;
••<4J;t-t
APPENDIX LL-1
REFERENCES
REFERENCES
LEMON LANE LANDFILL
1. Blasland & Bouck Engineers, P.C. for West inghouse E lec t r i c Corporat ion,Env i ronmenta l Technology Division. Supplemental HydrogeologicInves t iga t ion . Lemon Lane Landf i l l . June, 1987.
2. Powell, R.L. , for U.S. Env i ronmenta l P ro tec t ion Agency . Geology andHvdrogeo loqy of Lemon Lane Landf i l l . Monroe County . Indiana.Geosc ience R e s e a r c h Assoc ia tes Inc., December 8, 1982.
3. O'Brien & Gere Engineers, Inc., for West inghouse Elect r ic Corpora t ion .December 1982 and January 1983 Dri l l ing Logs for Monitor ing WellInstallation at MW-1S, MW-1D, MW-2, MW-3, MW-4S, MW-4I, MW-4D, MW-5, MW-6, MW-7, MW-8S, MW-8D and MW-9.
4. Blasland & Bouck Engineers, P.C., for Westinghouse Elect r ic Corporat ion,March and May, 1984. Boring Logs f rom Fill Borings B1-B8.
5. Blasland & Bouck Engineers, P.C., for West inghouse Electr ic Corporation,April, 1984. Landfi l l Cover Boring Program Logs.
6. Liang, T. for West inghouse Electr ic Corporat ion. Dra f t Air PhotoAnalysis Repor t , Monroe County , Indiana, Landf i l l Site 'C'. May 1983,Revised May 1984.
7. O'Brien & Gere Engineering for Westinghouse Electric Corporation, 1982.Magnetometer Survey Field Notes.
8. Blasland & Bouck Engineers, P.C., for Westinghouse Electric Corporation,Apr i l , 1984. Figures and Data, Seismic Re f rac t i on Survey Lines andSeismic Line Cross Sect ions, Lemon Lane Landfi l l .
9. Lillich, R. ' Inspect ion at Lemon Lane Landf i l l in Bloomington, Indiana,June 30 and July 1, 1984," Memorandum to Will iam Miner, EPA, July29, 1981.
10. Lillich, R. "Data Resul ts f rom Lemon Lane Landfi l l in Bloomington,Indiana," Memorandum to William Miner, EPA, September 9, 1981.
11. Lillich, R. 'Sampling at Lemon Lane Landf i l l in Bloomington, Indiana,'Memorandum to Will iam Miner, EPA, December 21, 1981.
12. Peoples, R., City of Bloomington Utilities, July 20, 1981. Letter to Ms.Dana Devole.
13. Indiana S ta te Board of Health, June and August 1981. Water andSediment Sampling Data.
11/8*9U88317A
REFERENCES (Cont'd)
14. B ieze, C. 'Indiana ITDD R5-8304-a Bloomington/Lemon Lane Landf i l l , 'Memorandum to EPA File, December 11, 1983.
15. Blasland & Bouck Engineers. P.C., for Westinghouse Electr ic Corporat ion,March and May 1984. Fill Boring Analyses.
16. Indiana University School of Public Environmental A f f a i r s , forWestinghouse Electric Corporation, November 1986. Analyt ical Resu l tsof Homeowner Wells Sampled Around Four PCB-Contaminated Sites.
17. O'Brien & Gere Engineers, Inc.. lor Westinghouse Electric Corporation.December 1982 and January 1983. Laboratory Analysis of Ground-WaterSamples (Wells MW-1S, MW-1D. MW-2, MW-3, MW-4S, MW-4D, MW-5,MW-6, MW-7. MW-8S, MW-8D, and MW-9).
18. O'Brien & Gere Engineers, Inc., for Westinghouse Electric Corporation.February 1983. Laboratory Analysis of Ground-Water Samples (WellsMW-1S, MW-1D, MW-2, MW-3, MW-4I, MW-4S, MW-4D, MW-5, MW-6, MW-7, MW-8S, MW-8D, and MW-9).
19. Gray, H.H., for EPA. July 16. 1981. Let ter to Dana Davoli, IndianaGeological Survey.
20. O'Brien & Gere Engineers, Inc., for West inghouse Electr ic Corporat ion,January 1983. Geophysical Logs (Gamma-Ray) for MW-1D, MW-4D, MW-5, MW-6 and MW-8D, and (Caliper and Gamma-Ray) for MW-2. MW-3,MW-7 and MW-9.
21. O'Brien & Gere Engineers, Inc., December, 1982, for West inghouseElectr ic Corporat ion, 1983 and Blasland & Bouck Engineers, P.C., forWestinghouse Electric Corporation, May, 1984. Ground-Water Elevations,Lemon Lane Landfill (Wells: MW-1S, MW-1D, MW-2, MW-3, MW-4S, MW-41, MW-4D, MW-5, MW-6, MW-7.MW-8S, MW-8D, MW-9, MW-B1, MW-B2,MW-B3 and MW-B4.
22. Indiana University School of Public and Environmental A f f a i r s , forWestinghouse Electr ic Corporation. Well Water User Survey Around FourPCB Contaminated Sites. November 1985.
23. Gates, G.R. Geologic Considerations in Urban Planning for Bloominqton,Indiana. Indiana Department of Conservation, Geological Survey, Reportof Progress 25, 1962.
24. Shaver et al. Compendium of Paleozic Rock Unit Stratigraphy inIndiana - A Revision. State of Indiana, Department of NaturalResources, Geological Survey, Bulletin 59, 1986.
25. Powell, R.L. Caves of Indiana. Indiana Department of Conservat ion,Geological Survey, Circular No. 8, 1961.
11/8/8911M317A
REFERENCES (Cont 'd)
26. Krothe. N. "F rac tu re Trace Ana lys is for the Lemon Lane Refuse Area ' ,Department of Geology, Indiana Univers i ty . 1982.
27. Krothe, N. for West inghouse E lec t r i c Corpora t ion , 1986. Solut ionFeatures, Surface Drainage, Lineaments, Sinkholes Data.
28. Hydroscience Assoc ia tes , Inc. for West inghouse Electr ic Corpora t ion .Prel iminary Report of Tracer Study: Lemon Lane Site Bloomington,Indiana. Low-Flow Test. February 26. 1988.
29. Westinghouse Environmental Engineering, February. March 1988. VariousMemorandum regarding, Site Reconnaissance, Lemon Lane Landfi l l ,February 1988.
30. G'ensky. N.E. for West inghouse Electr ic Corpor& t ion , March 5, 1986.Memorandum to G.W. Lee, Re: Field Work, West inghouse BloomingtonSites, February 1986.
31. McCann. M., Apri l 5, 1988. Memorandum to Wm. Sanner, Re: DyeTrace Schedule. West inghouse Environmental Engineering.
32. Hydroscience Associates, Inc. for Westinghouse Electric Corporation,September 1987. Falling Head Test Data for Well MW-1D.
33. West inghouse Environmental and Geotechnical Services, Inc., 'High FlowTracer Test, Lemon Lane Landfill, Bloomington, Indiana1, September 1989.
34. Quinlain, J.F., 1987. 'Quali tat ive Water Tracing with Dyes in KarstTerranes." Repr in ted f rom Prac t ica l Karst Hydrogeology with Emphasison Ground-water Monitoring, Course Manual, Nation. I Water WellAssociat ion, Dublin, Ohio.
35. U.S. Department of Agricul ture. Soil Survey of Monroe County. Indiana.1981.
11/8/891IM317A
APPENDIX LL-2
F5*g.
X
APPENDIX LL-2
POWELL REPORT. GEOLOGY AND HYDROGEOLOGYOF LEMON LANE LANDFILL
SUBTERRANEAN DRAINAGE FEATURES
Sinkholes:
The Lemon Lane Landfill, actually initiated as a refuse dump, was located
in a large enlongated compound sinkhole and on its adjacent eastern slopes
(Figure 3). The compound sinkhole consists of a sma11. valley with seve^a1
sinkholes in its bottom, as clearly shown on the Bloomington, Indiana 15
minute quadrangle (1908, scale 1:6?.500V Two major depressions are s^ov:n
w i t h i n the almost north-south oriu •, .. v a l l e y on the west side of the oreserily
landfilled area. The position of the sinkholes and their eastern slopes is
such that all surface drainage from the site was probably into these sinkholes
prior to use as a dump. The two sinkholes, as shown on the 1908 map, inc l u d i n g
the adjacent slopes within the large depression, would each have been about
30 feet deep.
The Bloomington quadrangle (1956, lh minute series, sclae 1:24,000) show
that the l a n d f i l l extended into and fille d the southernmost of the two sink-
holes in the small valley. The landfill had only partially encroached on
the northernmost sinkhole at that time. The partially filled North sinkhole,
as shown on the maps has a depth of 25 to 30 feet, but could have been
deeper prior to dumping of the f i l l materials.
The Lemon Lane Landfill or dump was utilized before modern sanitary
landf i l l standards were established in the area. Thus, there is l i t t l e doubt
that precipitation and surface draiange entering the f i l l materials descends
through the f i l l and enters the sinkholes.
There are several other sinkholes in the vicinity of the Lemon Lane
Landfill, none of which are known to receive any significant amount o* drain-
age from the landfill. A sinkhole pond adjacent to the northwest corner of
the l a n d f i l l , within the same compound sinkhole or valley as the two sinkholes
now under the landfill, may receive some seepage from the l a n d f i l l , but none
was noted during the time of field investigation. The compound sinkhole
valley extends southwestward from the site beneath the L. and N. Railroad
tracks to the Valhalla Memory Gardens where a few other sinkholes occur in the
valley bottom. The extent to which seepage from the landfill enters the f i l l
of the railroad grade or the sinkhole immediately beyond the tracks to the
southwest of the landfill is not known.
R. 2 W. R. 1 W
Bloomington, Indiana, Quadrangle1 5 minute ser ies , 1 908
Figure 3. The location of the Lemon Lane Landfi l l re la t ive to s inkholes prior
to use as a landfill. Scale about 1:24,000 or 1 inch to 2,000 feet.
Other sinkholes in the near v i c i n i t j of the Lemon Lane L a n d f i l l may
contribute surface drainage into the same subterranean groundwater syste™
as that from the landfill, but they do not receive surface drainage from
the landfill, so far as known. Some of these sinkholes in local yards and
lawns may have been partially filled with rock and earth, and some probably
contain small amounts of trash.
Sinking streams do not appear to be present at the site. The nearest
sinking stream is about one mile tn ' .''west of the site where a
surface drainage area of about 260 acres contributues stormwaters to swallow-
holes about 500 feet from Stoney Springs West (Figure 1).
Caverns:»No enterable caverns are known in the near vicinity of the Lemon Lane
Landfill, (Powell, 1961, p. 33-35). The nearest known cave is Stoney Springs
Cave, located about 14 miles to the southwest of the site, which is at thesouth end of the sinking stream valley mentioned previously. The cave is
very short and amounts to very little of the distance between the sinking
stream and Stoney Springs West. Neither the sinking stream nor the cave
have any known hydrologic relationship to subterranean drainage from the
Lemon Lane Landfi11.
A pit about 40 feet deep opening into a cave passage was reported by
Mr. Ralph Robertson on a h i l l s i d e across Stout Creek from the landfill (NWU,
NEhi, SEh», Sec. 25, T. 9 N., R. 2W). Another small cave has been reported
near the center of the west line of the XUk of Sec. 30, T. 9 N., R. 1W.,
also across Stout Creek from the site. Neither of these two caves should
have any hydrologic relationship to the Lemon Lane Landfill.
Springs:
Springs in the area mark the surfacing of groundwater that is for
the most part following cavernous routes through the fractured limestone.
All of the water entering sinkholes should be expected to follow fracturesand conduits in the limestone bedrock to resurgence or springs at lower
elevations.
Water from the spring designated here as the I l l i n o i s Central Spring
, SW^, SWs, Sec. 32, T. 9 N., R. 1 W.) that lies about 2,000 feet to
the southeast of the Lemon Lane Landfill was sampled, analyzed, and found
to contain PCB's prior to field work conducted for this report (Peoples,
1982, letter). Nine additional springs, including one stormwater rise or
wet weather spring, were found during field investigations in the area around
the Lemon Lane Landfill. The locations of these springs and estimates of
their size (flow) are give in Figure/ a^c* Table 1. The springs on the l i s t
that were flowing were sampled on 23 a\\c 19 July, 1982. An analysis of these
samples did not demonstrate any PCB's in any of the springs sampled, although
some other pollutants were recorded in most of the samples (see unspecified
reports to be prepared by Ecology and Environment, Inc.).
The fact that the Illinois Central Springs waters were contaminated with
PCB's in an earlier sample (Peoples, 1982, letter) was tempered with the
possibility that children in the neighborhood could have removed capacitors
from the Lemon Lane Landfill, salvaged useful copper from them, and left the
remains of the capacitors scattered over the area. The presence of PCB'sin the waters issuing from the spring, as opposed to a sampling of surface
runoff in the same locality, suggests that the PCB's are carried by the
underground waters.
The lack of PCB's in the Illinois Central Spring water sample from late
July 1982 may be owing to seasonal or otherwise differen hydrologic con-ditions that were not in effect during the initial sampling. The failure
to detect PCB's in the Il l i n o i s Central Spring during the sampling in late
July 1982, as well as the lack of their detection in any other springs in
the area, suggests that all the springs should be sampled again at a time
when the Illinois Central Spring waters are known to be carrying PCB's.
The Quarry Spring, owing to lack of access to the spring orifice and
considering also the very low flow associated with this spring, could be
dropped from the list of sample points. The Hinkle Spring, a wet weather
rise, should be sampled at a time when it is flowing inasmuch as it could
receive some subterranean stormwater overflow drainage from the site, so
far as is now known.
A Determination of Subterranean Drainage Routes from the Lemon Lane L a n d f i l l :
The exact direction of flow of all subterranean waters from the two
sinkholes on the west side of the landfilled area to specific springs is not
known at this time. There are several reasons, based on the data available
to date, for suspecting that not all of the drainage must flow to a single
spring. A generalized comparison of the flow from the I l l i n o i s Central
Spring with the flow of the Stoney Springs, for which a drainage area can
more readily be estimated, suggests '' ••' ''••• I l l i n o i s Central Spring drains
a relatively small area (Table 1). S i m i l a r l y , the volume of water issueing
from the three springs at the abandoned Bloomington Packing Plant suggests
that they drain an area about three times greater than that of the I l l i n o i s
Central Spring. The information available does not clearly prove that a
subterranean drainage divide does not exist at the site. The fact that none
of the springs contained PCB's during the late July 1982 sampling but both
the Illinois Central Spring and the Slaughter House Spring showed contarr-i-
nation with some other pollutants suggests that the waters could both be
derived from a somewhat similar source, such as materials dumped in sinkholes,
In addition, the source of stormwater discharge from the Hinkle Wet Weather
Rise could in part be in the vicinity of the two sinkholes in the landfill
area.
Table 1
SPRINGS IN THE VICINITY OF LEMON LANE LANDFILL
E & E, Inc., Field Flow cfs/Name of Spring Sample Number Estimate cfs Square miles
Stoney Springs East 1 1.3+ .28Stoney Springs West 2 1.5+ .32Illinois Central 4 .2Slaughter House 10 1.1-Packing House 11 .002PH Road 9 .7Snoddy 6 .03Detmer 7 .19+Robertson 8 .17Quarry 3 not flowingHinke Wet Weather Rise 5 dry
RESULTS OF PRELIMINARY BORINGS
Stratigraphy:
The four preliminary borings at the Lemon Lane Landfill penetrated
soils and mostly limestones and shales of the St. Louis Limestone, the
predominant surface bedrock in the area. Three borings were stopped HP the
lower part of the St. Louis Limestone (Borings 2, 3 and 4). Boring 1 was
into building stone units of the Sa^pn ' i>°s'ione. All of the borings
encountered some weathered fractun <• ,.LJcvng planes, as well as water
bearing units. Several voids were identified during d r i l l i n g , so^e of which
were filled with sediment, and others may have occured in. places marked as
core loss (descriptions of borings in Appendix and graphic columnar sections).
The soil in the four borings ranged from 7.5 feet to 22.2 feet in
thickness. The soil thickness in Borings 3 and 4 was 22.2 and 17.2 feet,
respectively, and may represent, in part, soil in crevices in the Mmestone.
These soils were reported to consist of red clayey silts, with some gravel and
residuum in places.
The highest bedrock stratigraphic unit recognized in the cores was a
chert zone assigned to the upper part of the St. Louis Limestone in Borings
2 and 4. It was also reported in a nearby water well (the Pelfree Well)
and is included on the cross sections. A seperate overlying chert zone in
Boring 2 was also assigned to the Upper St. Louis Limestone. A zone of
solitary corals underlying the beds containing the chert was easily
correlated between Borings 1, 2 and 4, but was not seen in Boring 3 (see
graphic columnar sections and cross sections, Figure 4).
Several shale layers of varying thickness were encoutered in each
hole, but none served as a marker bed. A particular bed of lithographic
limestone that is present below a prominant shale bed and above a "stink-
stein" unit served as another stratigraphic marker unit (see cross sections).
The shale was not of similar thickness in Boring 1. However, the same
shale may have been identified in a nearby water well (the Brown Well),
and has been included on the cross sections. The stinkstein consists of
micritic (very fine grain) limestone, dolomitic in part, with a fetid odor
when freshly broken. The odor is owing to natural organic contents in the
rock. Boring 3 apparently was stopped at a depth too shallow to sample
the stinkstein.
Boring 1 was drilled into rock easily recognizable as the b u i l d i n g
stcne (Indiana Limestone or Oolitic Limestone) of the Salem Limestone. The
exact boundary between the Salem Limestone and the overlying St. Louis
Limestone is not easily identified. The boundary is at the too of the beds
that contain a very small fossi\ ... • yra baileyi, which should occur about
midway between the top of the building stone and the top of the stinkstein.
Contrary to the geologic map compiled by Gates (1962, plate 1), the
Ste. Genevieve Limestone, the unit overlying the St. Louis Limestone, is not
present at the landfill site. The Ste. Genevieve may be present in the
vicinity at elevations some 30 feet above where indicated by Gates and there-
fore is of more limited areal extent than shown on his map.
Structure:
Structure contours were plotted on two stratigraphic horizons identified
in the borings at the Lemon Lane Landfill. One map was prepared to indicate
the strike and dip or slope on both the coral zone that was identified in
three borings as well as that of the lithographic unit below the shale and
above the stinkstein identified in all four borings (Figure 5). The
different altitudes on the coral zone indicate a slope to the southwest(dotted lines on Figure 5), while the different altitudes on the lithographic
limestone bed show a dip to the south (solid and dashed line on Figure 5).
Both dip directions are plausible owing to a thinning in a northwestward
direction of the strata between the two selected layers. The dip of the
strata could vary considerable within a short distance of the control
points or boring data available at the Lemon Lane Landfill, as might be
shown by acquiring additional data.
The fractured and jointed nature of the bedrock is evident in various
rock exposures, mostly in road cuts and quarries, in the area to the north
and northwest of the landfill. Some fractures were seen in rock in the
cores and are noted in the descriptions of the cores (Appendix) and shown
Q
V A L H A L L A M E
All well locllions er> appronmale
Figure 5. Altitudes of marker beds from boring data at Lemon Lane Landfill.Dotted lines on coral zone, solid and dashed lines on a
lithographic limestone unit.
on the graphic columnar sections. The relative close spacing of joints
and other fractures in St. Louis Limestone and similar strata of the upoer
part of the Salem Limestone are condusive to downard and lateral movement
of subsurface water. Those fractures that have carried water are commonly
weathered and some are enlarged by solution of the limestone along the
fractures. Weathering and solution features are also noted in the descrip-
tions and on the graphic columnar sections.
Hydrology:
The four borings at Lemon Lane Landfill are each completed as water
level monitoring and water sampling points. Boring 1 was drilled into the
upper part of the Salem Limestone. Boring 2, 3 and 4 were stopped in the
lower part of the St. Louis Limestone. Boring 1 was completed as a monitoring
well to sample the upper part of the Salem Limestone, therefore it should
not be representative of the same groundwater zone measured or sampled in
Borings 2, 3 and 4 (see Figure 4). Boring 2 was completed as a well to
sample only that part of the lower St. Louis Limestone that is approximately
at the same level as the Illinois Central Spring (see Figure 7). Borings3 and 4 were completed to monitor and sample all but the top few feet of
the bedrock and the overlying soil.
A measurement of water levels was made for each of the four wells on
27 October 1982 by E and E Inc. geologists (telephone communication) as
presented on Table 2. A general water level for the landfill is represented
by only three datum points (Borings 2, 3 and 4) as shown as Figure 6.
The water level measured in Boring 3 following development of the well
is nearly the same as the bottom of the boring. Difficulty in developing
this well casts some doubt as to the validity of the water level data
(E and E, Inc., Ron St. John, telephone message).
The three datum points shown on the water level map indicate that the
slope of the water table is to the northwest. This slope is reasonable to
expect in view of the ridge top location of the landfill in relation to
the deep adjacent valleys and known spring outlets for groundwater (see
Figure 1). However, the groundwater slope as calculated and shown is away
Q
<•" '" X
•!?
B3K 95
Do05 D
° Pon^N )
»•'"'}}
D °°n E
'/'^V^'Union / | \\
0| • 81696
j f
i~(— i
Q ia
i ~Pel l tee "
oC
/
L A N D F I L L X
1
> / x
. b* Biown
<D
h°0
All »»H locations are
Figure 6. Approximate groundwater level as calculated from the water leveldata indicated for Boring 2, 3 and 4 at L^mon Lane. Data from
E & E I, Inc.
\\
from the I l l i n o i s Central Spring, which is reported to have carried PCB
wastes from the landfill area. The water level at Boring 2, which was
completed below a thick shale layer and thus excludes open drainage from
the overlying bedrock as compared to Borings 3 and 4, may represent a
separate and lower groundwater zone than that in Borings 3 and 4.
Table 2
WATER LEVELS AT LEMON LANE LANDFILL
Boring
B-l
B-2
r* _~>
B-4
Brown
Pelfree
1.
2.
Groundlevel -,E & El1
92.83
117.07
99.67
119.98
100 BM takentracks North
Topographic
Topo2
862.85(863)
887.09(887)
869.69(870)
890
885
881
for orangeof Boring
base taken
TopOuterCasing
94.84
118.27
101.43
122.99
spot on top2.
as 890 feet
Topcasing to ^
Water Level
48.4
64.a
56.5
76.05
of rock North
as! at Boring 4
• Groundlevel to
Water Level
46.29
63.2
54.74
7?. 04
60
60
of L and N
from 1 inch
ComputedAltitude ofWater Leve'
816.56
8?3.S9
814. Q5
816. Q6
815
821
3.
to 400 feet, 4 foot contour interval, map of Bloomington, Indiana,with adjustments for Borings 1, 2 and 3 from E & El Survey data.
Water level measurements by E 4 El personnel on 27 October 1982,(reported by telephone by Ron St. John).
The water levels reported in the borings occur at positions (about 10
feet to 20 feet) below the calculated positions of the bottoms of the two
sinkholes now buried in the Lemon Lane Landfill (Figures 3 and 7). The
bottoms of the two sinkholes were calculated to be at an altitude of about
830 feet asl, or at least below the 840 foot contour (Figure 7). Surface
drainage into the sinkholes most likely descended through solution enlarged
fractures to a nearly horizontal conduit at or near the water table withina close proximity to the bottoms of thr- -;n',holes. The presence of the
sinkholes predicates the existance of a conduit or easy flow path for the
groundwater away from the bottom of the sinkholes. Conduits or subterranean
passages from several sinkholes could unit as tributaries to form a single,
usually larger, conduit or cavern passage. The main conduit or passage
commonly carries the subsurface drainage to a spring outlet that is tributary
to a surface stream in a nearby valley.
The subterranean conduits function much the same as surface streams,
except that they are roofed or enclosed such as to effect flood flows diffe-
rently than surface streams. Unlike surface streams that overflow their banks
during flood stages, subterranean conduits f i l l to a capacity and then stack
water to the point or level at which it backs up into sinkholes or overflows
into higher, normally dry, subterranean passages. The floodwaters in higher
routes do not always discharge to the same spring as the normal flow levels.
Similar to surface streams, the subterranean conduit should serve as a
low point for water in fractures or smaller solution enlarged voids in the
adjacent and supraadjacent bedrock. That is, the groundwater in the adjacent
rock higher than the conduit should flow towards and into the conduit. Thus,
a conduit may be associated with a sag or depression in the water table,
except perhaps during a flood stage.
The higher water table position in Boring 2 appears to rule out the
probability that this boring is into or along a direct hydrologic route
between the Illinois Central Spring and the Lemon Lane Landfill. The lower
groundwater level reported in Boring 1 would suggest that it is nearer any
subterranean route between the landfill and the Illinois Central Spring.
Boring 1, however, is completed in a deepr groundwater zone. The fact that
PCB's were reported at the I l l i n o i s Central Spring is the sole evidence for
assuming that groundwater movement could be from the Lemon Lane Landfill to
the spring. The fact that no PCB's were reported from the analysis of the
28 and 29 July, 1982 samples from many springs in the area, including the
I l l i n o i s Central Spring, is inconclusive. The possibility remains that "low
flow is in one direction and that some flood waters flow to another soring.
The fact that the pond shown i"i • >.•!.: naps (the 1956 Bloomington
quadrangle and 1976 city map) was not shown on the 1908 Bloomington quadrangle
suggests that the pond was either too small to be shown in 1908, or that the
pond may have been subsequently man made. Regardless of origin, the pond is
apparently 30 to 40 feet above the groundwater level measured in Boring 3.
REFERENCES CITED
Gates, G.R., 1962, Geologic considerations in urban planning for Bloomington,Indiana: Indiana Geological Survey, Kept. Progress 25, 21 p.
Malott, C.A., 1922, The Physiography of Indiana: j_n_ Handbook of IndianaGeology, Indiana Dept. Conservation, Pub. 21, pt. 2, p. 59-256.
Powell, R.L., 1961, Caves of Indiana: Indiana Geological Survey, Circular8, 127 p.
, 1976, Some geomorphic and hy<;r'. ' ;,c implications of jointing incarbonate strata of Mississippian Age in south-central Indiana:unoublished Ph.D. dissertation, Dept. of Geosciences, Purdue Univ., 168 p.
RECORD OF SUBSURFACE EXPLORATION
Boring.
A l t & W l t z l gE n g i n e e r i n g , I n c .
I ' I U ^ L I Nmu. twit tan* t«ijr*jj n . t p n t B o r i n g 7-^-s:, r-::-5.-
S,le Bloomington, Indiana P r n j a r l Nn S2072-C1
Dts:niniDi
'Da rk Gray Clay'ey S"ILT with^\ ? one Large Gravel
-d ish Brown Silty CLAYr wi in some Limestone
FragtDents
'_ Gray LIMESTONE
- Interbedded Layers of Reddish- Brown CLAY and Limestone• Floaters
- Gray LIMESTONE withNumerous Clay Seams
(Rock Core Logged and Classified1 by EEI Geologist)
i
(Continued on next page)
O f H H
-<
c, m
in •
15 •
20 •
25 •
30 •
35 •
40 .
45 •
SAUPlf
1SS
_'Si
3SS
4SS
^IRC^
xx/^ 2 R C ,
3RCX
X*' >*
A R C X
X' ^^
5RCx
-<xs ss
r6RCx
r7RC"''^ >/,8RCX
//
^RC/XX
10RC'
^
Blou-s per 6"In crenent
3-5-7
1-3-3
4-4-6
7-50/1"
Dr i l l e r ' s Remarks
Rock encounte red at11.2'.1st Run 11.2' to 13.1'. .100% Recovery
2nd Run 13.1' to 16.8' . •1* Recovery (numerousClay Seams)3rd Run 16.8' to 19.5' . -No Recovery
4th Run 19.5' to 2 6 . 8 ' . "
5th Run 26.8 ' to 30.8'. '_100% Recovery
•
6th Run 30.8' to 34.8' . ~_100% Recovery
7th Run 34.8' to 36.3' . m
100% Recovery8th Run 36.3' to 37.8' . .100% Recovery
9th Run 37.8' to 41 .2 ' . -100% Recovery •
10th Run 41.2 ' to 4 6 . 3 ' .-100% Recovery
RECORD OF SUBSURFACE EXPLORATION
B-l (Page 2)
Alt k u i t z i gEne 1 neer ing , Inc
Pio jec t
Site
Lemon Lane Landfill
Bloomington. Indiana
Date ol Boring
Project No :
7-16-82. 7-21-82
S2072-C
D E S C R I P T I O N
1-
i
Gray LIMESTONE with numerousClay Seams
(Rock Core Logged and Classifiedby EEI Geologist)
i
1
i
-
i
(Continued on next page)
DCTH
™
50.
55 .
60 •
™
65 .
70 ~
75 •
80 ~
85 ~
90 I
SiMPlI
' 10RC
,1
11RC
^^^- —
^
^^>
^d-
^
^ ^^%>15RC"-v^
^
ilovs per 6"I n c r e m e n t Dri l ler ' s Renarks
10th Run 41.2 ' to 4 6 . 3 ' . -IDO'i Recovery
lltli Run 46.3 ' to 55.7 ' . -100% Recovery •
12th Run 55. 7' to 65 .7 ' -100% Recovery •
-
13th Run 65.7 ' to 75.7 ' "1002 Recovery "
14th Run 75 .7 ' to 86 .7 ' .'1002 Recovery
15th Run 86.7' to 95.8' . \1002 Recovery
RECORD OF SUBSURFACE EXPLORATION AH {. w
Boring B-l (Paee 3)
Pro iec l Htmt Lemon Lane Landf i l l
SUB ? nnTrri not nn. Indi ana
Dale Of Boring 7-16-82. 7-21-82
Project No S2072-C
OE5CHIPTIOI
-.rav LIMESTONE with• • : rous Clay Seams
(Rock' Core Logged and Classifiedby EE1 Geologist)
•
- Boring terminated at 101.2 feet.
1
^
1 Water encountered at 41.0 feetwhile drilling.
i
•
OIPTH
-
95 •••
100 •
-
105 •
110 .
m
m
m
stunt'/'*
x<JS
/^/
////
16RC
^/
Blows per 6"I n c r e m e n t Dr i l l e r ' s Remarks |
J
15th Run 86 .7 ' to 95 .8 ' . "100% Recovery
-
16th Run 95.8 ' to 101.2' .100% Recovery
-
-
-
m
•
RECt)RD OF SUBSURFACE EXPLORATION Alt & uitzigEngineering, Inc.
Project Name Lemon Lane Landfill
Bloomington, Indiana
Date of Boring
Project No :
7-21-82, 7-26-82
S2072-C
DESCRiPTiOl
JUflFiCl
u Bro'.-n Clayey SILT
, _j is : i Brown CLAY withi t r a c e Limestone Fragments
" Gray LIMESTONE with OccasionalClay Seams
(Rock Core Logged & Classifiedby EEI Geologist)
i
i Very Soft Green SHALE
(Continued on next page)
OtPTM
-
c a
10 •
15 •
20 •
25 •
30,
35 •
••
40 •
45 •
SAMPlf
1SS
_ . . '.>
3SS
IRC'
2RC^
3Rc"S ^s
ARC -
SRC ^S ^^
/'S
• 6RCX
S^S/ S
s/,'/,7RCx
^x"8RCs '9RC^
'//,1CT;C
Blows per 6"Inc rement
3-4-4
2-2-2
7-7-9
Driller 's Remarks
•
1st Run 7.5' to 1 2 . 2 ' . ~100% Recovery
2nd Run 12.2' to 16.7'. -100Z Recovery •
3rd Run 16. 7 ' to 2 2 . 2 ' . _100% Recovery •
4th Run 2 2 . 2 ' to 26 .7 ' . _100% Recovery .
5th Run 26.7 ' to 31.0' . "100% Recovery
6th Run 31.0' to 36.3'. -100% Recovery •
7th Run 36.3' to 41.2'. _100% Recovery (
8th Run 41.2' to 4 2 . 2 ' . '100% Recovery9th Run 4 2 . 2 ' to 44 .0 ' . '100% Recovery10th Run 44.0' to 45.6'. '15% Recovery
RECORD OF SUBSURFACE EXPLORATION
Bowing B-2 (Pace 2^
Lemon Lane Landfi l lProject Name .
5i tg Blooming ton, Indiana
Date 0< Boring
Project No :
Alt & W U z l gE n g i n e e r i n g , I n c .
7-21-82. 7-26-82
S2072-C
D E S C R I P T I O N
iVc-ry So f t Green SHALE
•
~
•
-
- Gray LIMESTONE with OccasionalClay Seams
(Rock Core Logged & Classified• by EEI Geologist)
•
-
- Boring terminated at 80.0 feet.
- Water encountered at 66.7 feet• while drilling.
i
DtPTM
-\
50.
55.
~
60 i
-
65 .
70 .
75 .
an
85 ;
•
SAMPLE
10RC-
^ J] 1 r' •"
12RC^
^ ^13RC -
sS
14RCX
^ ^15RC^
%16RC
17R(f
LI SRC
. 19RC
//• 20RC
Blows per 6"Increnent Dril ler 's Recarks
10th Run 4 4 . 0 ' to 45 .6 't p mi vtli/4 Recovery
llth Run 45 .6 ' to 4 7 . 4 ' -10% Recovery
Du-Cone 47 .4 ' to 52.8 ' "through very sof tgreen Shale
12th Run 52 .8 ' to 56.5' B
100% Recovery
13th Run 56.5 ' to 58.8' "100X Recovery
14th Run 58.8' to 6.1.6' •1002 Recovery-
15th Run 61. o to 62 .6907. Recovery
Du-Cone 62.6 ' to 68.2'through so f t green Shale.
16th Run 68 2 ' tn 69 0100% Recovery
17th Run 69.0' to 72.0 ' !100% Recovery
18th Run 7 2 . 0 " to 73.0' ~100% Recovery
19th Run 73.0' to 76.0 ' "70% Recovery
20th Run 76.0 ' to 80.0' -75% Recovery
«
WELL DIAGRAM
Ground Surface
Guard Pipe
Cement Grout
Bentonite Seal
Well Screen -/ —
Granular Fill
Bentonite Seal
Granular Fill
Bottom of Bore Hole
Project: Lemon Lane Landfill
Bloomington, Indian
Well No. B-l
Time & DateStarted: 7-26-82 3:30 p . m .
Time & DateCompleted: 7-27-82 1:30 p .m .
Driller's Remarks:
Prepared For:Ecology and Environment, Inc.CMeseo. IllinoisPRCJiCI K»Mf
Lemon Lane LandfillBloorainRton, Indiana
sPrepared By:Alt & Witzig Engineering, Inc.IndianaPolis > Indiana
PROJECT NO OAT{
WELL DIAGRAM
0.0 FT
Bentonite Sea
Granular Fill>
Well
.FT
Bottom of Bore Hole
Project : Lemon Lane L a n d f i l l
Bloore inp ton , I n d i a n a
Well No: B-2
Tim? & DateStarted: 7-26-82. 1:30 p.m.
Time & DateCompleted: 7-27-82. 9:45 a.m.
Driller's Remarks:
Prepared For:Ecology and Environment, Inc.Chicago, IllinoisPftOJtCT IAUILemon Lane LandfillBloomineton. Indiana
Prepared By:Alt & Witzig Engineering, Inc.Indianapolis, IndianarvcufCT to
S2072-C
DAT!
08/82
RECORD OF SUBSURFACE EXPLORATION Alt & v„ , E n g i n e e r i n g , Inc
Lemon Lane Landfil lProject Name _
Site Bloomington, Indiana
Date o1 Boring
Project No :
7-27-62. 6-2-6?
S2072-C
DISCRETION
f r o w n Moist Clayey SILT
1 Brown to Red CLAY withOccasional LimestoneFragments
-
1
" Gray LIMESTONE with numerousClay Seams & Soft Shale Layers
(Rock Core Logged and1 Classified by EEI Geologist)
-
1
i
(Continued on next page)
DtriM
.
-
5 «
10 ~
15 i
20 '.
-
25 '.
30 m
35 I
40 ~
45 i
SiWPLE
1SS
IRC", "
2>.c j••-^^
^^4RC"
5RC"^-^
bRC -
ilows per 6"Inc remen t
4-3-4
Dril ler 's Remarks
-
-
Encountered rock at 22. 04
1st Run 2 2 . 2 ' to 23 .7 '80% RecoveryTri-coned through softclay seam, 2 3 . 7 ' to 25. 2_2nd Run 25.2 ' to 25 .6 ' ~No RecoveryTri-coned through softf * T a \ j cpam 9S fi T fn 9Q fi1
3rd Run 29 .6 ' to 32.6' -100% Recovery
4th Run 32.6' to 36.2' "1002 Recovery
5th Run 36.2' to 38.4' -1002 Recovery
Tri-coned through soft •clay, 38.4' to 43 .6 '
6th Run 43.6 ' to 49.6 ' -1002 Recovery •
RECORD OF SUBSURFACE EXPLORATION Alt i w i t z i gEngineering, Inc.
Bonny B-3 (Page 2^
Project Kame Lemon Lane Landfill
$,te BlootPlneton, Indiana
Dete of Boring 7-27-82. 8-2-82
Project No S2072-C__
D t S C B I F T I O H
-
Gray LIMESTONE with numerousClay Seams & Soft Shale Layers
(Rock Core Logged and• Classified by EEI Geologist)
Boring terminated at 59.7 feet .
•
i
>
DFPTH
—
50.
._
55.-
-
bU .
65.
•
•
•
SAMM
^^
' f ' r ' _ •
^^7RC'^ "
s "^ .
^^ ' , SRC-
slows per 6"Increment Dri l ler 's Remarks
6th Run 43.6 ' co 49 .6 ' _100% Recovery
7th Run 49.6 ' to 55.9 ' .100 X Recovery _
•8th Run 55.9 ' to 5 9 . 7 ' '100% Recovery
_
•
WELL DIAGRAM
Cement Grout''
Bentonite Sea
Granular Fill
Well
Bottom of Bore Hole
FT.FT
Project: Lemon Lane Landfill
Bloomington, Indiana
Well No: B-3
Time & DateStarted: 8-2-82. 5:00 p.m.
Time & DateCompleted: 8-3-82, 9:00 p.m.
Driller's Remarks:
Prepared For:Ecology and Environment, Inc.Chicago, Illinois
KICJECl DAME
Lemon Lane LandfillBloomington, Indiana
Prepared By:Alt & Wi tz ig Engineering, Inc.Indianapolis, IndianaPKOJKT 10
S2072-C
lorn
08/82
RECORD OF SUBSURFACE EXPLORATION
M • n /Bonng B-4 _
Alt i u i t z i gE n g i n e e r Ing , Inc .
Vnmr Lemon Lane Landfi l l
Site Bloomington, Indiana
Date o< Boring
Project No :
8-3-82, 8-5-82
S2072-C
DISCBIPTIDI
-
-eddis,h Brown Silty CLAYto Clay
i
, '
-
•
Gray LIMESTONE
Rock Core Logged andClassif ied by EEI Geologist)
i
•
i
(Continued on next page)
DIPTH
5.•"
10 •
15 ~
20.
"i30 •
35 ~
^
40 •
45 ~
SAHPl!
s s"
K
• IRC"
&
^//////<
' S
//-<>//
^
Blows per 6"Inc remen t Dr i l le r ' s Remarks
-
""
-
Encountered rock at16.4' "
Tri-coned to 17 .2 'through weatheredLimestone
1st Run 17.2' to 26.3 ' .100% Recovery
2nd Run 26.3' to 36.3' m
100% Recovery
3rd Run 36.3' to 46. 3' -1002 Recovery •
-
-
RECORD OF SUBSURFACE EXPLORATION Alt & w i t z l gE n g i n e e r i n g , I n c
Boring B-4 (P.- -e 2)
Lemon Lane Landfil lP/o jec t Kerne
Site Bloomington . Indiana
Dale ol Boring 8-3-82, 8-5-62
Project No • S2072-C
DtSCRiPTiOl
;_
r
' Gray LIMESTONE
(Rock Core Logged and1 Classified by EE1 Geologist)
.
•
-
•
- Boring terminated at 86.3 fee t .
Water encountered at 62.0 feet .
DfPTH
i
50 •
55 .
60 .
65 '.
70 .
75 .
80 j
85 ;
90 .
SAMflf
3RC
^4RC"
^5RC^
<^
6RC^-
^
^
7J(C^
%
Jlows per 6"Inc remen t Dril ler 's Remarks
3rd Run 36.3' to 46. 3' _100% Recovery
4th Run 46.3' to 56. 3' "100% Recovery "
•
5th Run 56.3' to 66.3' "1002 Recovery "
6th Run 66.3' to 76 .3 ' '100% Recovery. "
7th Run 76.3' to 86.3' '100% Recovery
--
•
WELL DIAGRAM
Bentonite
Granular Fill>l
Well Screen4r*t=
Bottom of Bore Hole
Project : Lemon Lane L a n d f i l l
B loon ing ton . I n d i a n a
Well No: B-4
Time & DateStar ted : 8-5-82. 11:00 a .m .
Time & DateCompleted: 8-5-82. 3:00 p.n.
Driller's Remarks:
Prepared For:Ecology and Environment, Inc.Chicago, Illinois
PROJECT kAUELemon Lane LandfillBloomington, Indiana
Prepared By:Alt & Witzig Engineering, Inc.Indianapolis, Indiana
PftOJECT 10
S2072-C
DATE
08/82
Legion Lane Landfill Boring 1
Monroe County, Indiana Bloomington QuadrangleSWs, SE*s, NEJj, Sec. 31, T. 9 N., R. 1 W. , Second Principal Meridian111 EL, 2760 SI, Sec. 31, T. 9 N., R. 1 W.Lat. 39° 10' 19" N., Long. 32° 33' 36.5" W.
Altitude (topographic) 866 corrected to 863Ground level 92.83Top inner casingTop outer casing 94.84Total depth 101.2
1 0-1.5 Red clayey silt, residuum of gravel (E & E Log).
2 1.5-11.2 Red clayey f , i : : . .i, ic^um of gravel (E & E Log).
3 11.2-14.0 Limestone, yellowish gray 2.5Y 6/1, micritic, or microcrystal1 "black silicious corals at 13.1-13.2, hard and dense, but breakseasily along numerous low angle silty streaks, grayish oli v e 5Y6/2, contains several scattered low angle stylolites (low anglemay indicate a tilted or slumped block of limestone); red mudalong low angle bedding plane at 11.5; crumbly low angle breakin silty streaks at 12.8; fresh stylolitic break at 13.1 withglauconite streak; high angle fracture with red clay 13.4-13.55
4 14.0-19.5 Clay reported (not seen).
5 19.5-20.05 Limestone, grayish yellow 2.5Y 7/2 to 2.5Y 7/1 light gray.micritito microcrsytalline, dull luster, hard and dense, weathered siltystreaks at top.
6 20.05-26.8 Clay; solution surface on top of underlying limestone.
7 26.8-32.0 Limestone, dolomitic (slow fizz), pale yellow 2.5Y 8/3 to lightyellow 2.5Y 7/3 with light gray 2.5Y 8/8 at top, nicritic to"finely crystalline, bands at 27.2 and 27.7, hard and dense;long white calcite annealed vertical fractures in places; redclay at 27.3 h inch thick; badly weathered zone (soft) 30.5-30.7.
8 32.0-33.4 Limestone, grayish yellow 2.5Y 7/2 to 2.5Y 6/2 fine-grain cry-stalline (sparite), some scattered fossils (pecten-like), withglauconitic (greenish gray) 10GY 6/1 splotches in fine crystal1^-areas at top, and changing to earthy luster micritic 2.5Y 8/2,towards base transitional boundary; weathered earthy lusterlimestones at 32.3-32.35.
9 33.4-36.3 Limestone, dolomitic (slow fizz), light gray 2.5Y 8/?, micritic,earthy luster, hard and dense; bedding plane with red clay at33.8 (some loss of core in previous 3 units).
10 36.3-37.2 Shale and limestone: limestone similar to above with lightgreenish gray 10GY 7/1 shale, calcareous, convoluted beds orweathering cavities in upper part; calcareous shale only in lowerpart.
11 37.2-38.15 Limestone, dolomitic, yellow 2.5Y 8/6, micritic, soft; deeolyweathered, WET ZONE.
Lenon Lane Landfill Boring 1
12 38.15-11.50 Limestone, dull yellow orange 10YR 1/2 to 10YR 7/3, m i c r i t i c , wi:scattered small grey pebbles, dull luster, hard and dense,stylolite at 38.80; vuggy with solution enlarged cavities to 1"-wide in upper .5 foot; white patina to chalky debris in vuggy zo-at 40.3, 40.85 and 41.0 to 41.4; friable vuggy zone at 41.1 to41.4; closed vertical fracture 41.0+ to 41.?, high angle, fracturt41.35-41.50.
13 41.50-45.0 Limestone, grayish yellow brown 10YR 6/2, nicrit^c to lit^ccv^:1
hard and dense to brittle; very steep inclined joint 41.50 '.41.80, vertica1 ^ - •" '1-?.35 to 43.3; vuggy zone 42.7 to £?.".
M 45.0-45.6 Limestone, grayish yellow brown 10YR 6/2, micritic, du 1!hard and dense; deeply weathered ("punky") 45.2 to 45.5 alonevertical zone; bedding plane solution at base of unit.
15 ' 45.6-46.0 Limestone, dull yellow orange 10YR 6/3, micritic, lithographic,hard and dense, very brittle, includes numerous l i g h t smallangular grains; iron stained and solution pitted vertical joint45.8 to 46.0.
16 46.0-47.6 Limestone, dull yellow orange 10YR 6/3, micrHic, d u l l luster, haand dense; bedding planes weathered at 46.65, 46.85, 46.95 withsome solution, 47.54 with solution enlarged openings , 47.6 withsolution openings; low angle fracture with solution 47/25-47.30including iron stained rind; vertical fractures annealed withcalcite 46.0 to 46.55, dissolved calcite 46.55 to 46.8.
17 47.6r48.1 Limestone, dark grayish yellow 2.5Y 5/2, micritic to microcry-stalline, hard and dense, with white to clear crystalline patchesvuggy, with solution enlarge bedding- plane at top, 47.85 to 47.8 *48.1 has large (3/4 inch) solution voids.
18 48.1-48.6 Limestone, grayish yellow 2.5Y 6/2, micritic or lithographic, hareand dense, brittle; lighter streaks at 48.3-; vuggy bedding planesolution at about 48.2, 48.3 and 48.6; solution widened, ^ronstained inclined fracture 48. 1-48. 2-; and vertical fracture 48.3-'48.6.
19 48.6-50.05 Limestone, light yellow 2.5Y 7/3, micritic, dull luster, hard anddense, darker sand size grains in places, calcite annea^d vertic;fracture in top part of unit.
20 50.05-50.35 Shale, light gray 5Y 7/1, indistinctly bedded, with glauconiticspots and streaks, calcareous, soft.
21 50.35-50.45 Limestone, yellowish gray 2.5Y 6/1, micritic, solution along beddi'planes top and bottom.
22 50.45-52.0 Limestone, yellow gray 2.5Y 6/1, micritic, dull luster, hard anddense, bottom .15 silty and shaly.
23 52.0-52.3 Limestone, dolomitic (slow fizz), grayish yellow 2.5Y 6/2,micritic, dull to earthy luster, hard and dense; few small vugs irtop.
Lemon Lane Landfill Boring 1
24 52.3-53.9 Limestone, light gray 2.5Y 8/1, rrp'critic, dull luster, hard anddense; numerous small vugs in upper part decreasing downward;possible weathered bedding planes at 52.8 and 53.0.
25 53.9-55.1 Limestone, light gray 2.5Y 8/1, micritic, chalky luster, hardand dense; weathered high angle fracture 54.0-54.15; weatheredsteeply sloping fracture 54.3-54.6; deeply weathered to solutionenlarged vertical fracture 54.6-54.8; solution on bedding o^ane54.85; basal bedding plane weathered.
26 55.1-56.2 Limestone, ye 11 ru-•• • '' <ir?.y 2.5Y 5/1, micritic to nicrocrystal 1;- .hard and dense, •.,- .-^stein," grades downward to laminated s^1',,.grayish yellow 2.5Y 6/2 at 55.41; then to yellowish gray 2.5Y5/1, with an organic zone at 55.75 brownish black 2.5Y 3/1; basalpart vuggy 55.9-56.2; several pieces of core reversed and out of
place in this unit.
27 56.2-59.55 Limestone, dolomitic (slow fizz), gray 5Y 5/1 to light gray 5Y 7/1at top, micritic, dull luster, hard and dense, "worm tracks"in places, unevenly laminated in part.
28 59.55-60.0- Clay shale, calcareous, light gray 2.5Y 8/1, laminated 59.55-59.65but blocky fracture, nonlaminated, with irregular vertical blackstringers 59.65-60.0--
29 60.0--60.5- Limestone, gray 5Y 5/1, fine crystalline to micritic, hard anddense; top shaly; bottom grades into underlying shale.
30 60.5--60.7- Shale, gray 5Y 6/1, finely lamined, soft.
31 60.7--66.8- CORE LOSS
32 66.8--67.20- Limestone, same as 60.0-60.5; top grades upward into shale; bottorrcontact sharp with underlying unit.
33 67.20--67.30- Limestone, shaly, organic, dark grayish yellow 2.5Y 5/2, finelylaminated, hard and dense, somewhat fissil.
34 67.30--67.85- Limestone, light gray 2.5Y 3/1, micritic, earthy to chalky luster,soft.
35 67.85--67.9- Limestone, olive black 5Y 3/1, finely laminated but not fissil,hard and dense.
36 67.9--72.3 Limestone, gray 5Y 6/1, micritic, dull to very dull luster,unevenly laminated in part, large weathered iron stained and vuggycoral in top; vertically fibrous sparry lens (celestite) at 69.3and sparry lense at 69.65 and sparry band at base of unit inthin organic shaly zone.
Lemon Lane Landfill Boring 1
37 72.3-77.2 Limestone, gray 5Y 5/1, micritic to microcrystal1ine, fossi 1 iwith calcite f i l l i n g , organic shaly in top .05+; slightly fetidin bottom 1.7 feet, base of unit black organic shaly; small vugscommon 74.1-74.3.
38 77.2-79.1 Limestone, gray 5Y 5/1, micritic and microcrystal1ine to mediumcrystalline, slightly fossi1iferous, glauconitic color to somecrystalline calcite spots; unit contains numerous small vugs,some crumbly areas.
39 79.1-81.2 Limestone, yellowish aray 2.5Y 6/1, micritic to microcrystal 1<n^.includes num^-- calcite spots "eyes," lower contactgradational; siyIDMtes at top and 79.45; vuggy in places, 79.2-79.8 and 80.7-80.8; slightly weathered vertical fracture 79.6-80.4.
40 81.2-82.7 Limestone, light gray 10YR 8/1, micritic, clayey to silty, earthyluster, hard and dense dark stringers, bottom .6 (82.1-82.7) withcontorted laminations of darker silty streaks; CELESTITE band at82.5.
41 82.7-83.15 Shale, to shaly limestone, dark grayish yellow 2.5Y 5/2, hard anddense but parts readily, fossiIferous.
42 83.15-84.2 Limestone, light gray 7.5Y 8/1.with greenish mottles ,-micritic ,dull luster, several sets of graded very fine grain beds about .2thick i, small granular pyrite nodules as "eyes" in places,spotty as small lenses in other places.
43 84.2-86.7 Limestone, greenish gray 10GY 5/1, micritic,fine!y laminated withsilty streaks, possibly micaceous on silty streaks, clayey glauconitic bands up to 1/8" in lower .15 foot.
44 86.7-87.5 Limestone, dark greenish gray 10GY 4/1, micritic to microcrystal-line, but laminated in part, includes white irregular sparryinclusions, some lenticular, bottom .1 shaly; vug at top-includes quartz crystals and possibly small ankerite crystals.
45 87.5-91.4 -Limestone, light gray 5Y 8/1 to 5Y 7/1, some darker splotches,micritic, d u l l luster, hard and dense but parts on silty streaks,laminated for most part, contorted and includes green siltymaterial from above unit in top .2 foot, possible vertical fractu88.4-38.8;- vuggy at 91.1 and 91.2; some "dollars" from rotatingpartings during d r i l l i n g .
Lemon Lane Landfill Boring 1
46 91.4-92.05 Limestone, light gray 7.5Y 7/1, micritic with very small crysta1-line inclusions, mostly dark inclusions and numerous small(macroscopic) vugs, laminations in base of unit contorted.
47 92.05-94.8- Limestone, grayish yellow 2.5Y 7/2, micritic, dull luster, hardand dense, indistinctly laminated, breaks across laminations,bottom contact color gradational.
48 94.S--97.2 Limestone, gray 5Y 5/1, micritic, dull luster, laminated but Kv •and dense, breaks across laminations.
49 97.2-97.6 Limestone, ol : > - bands 5Y 3/1 in lighter gray m a t r i x , 1.-..amplitude stylo li t e with three graded zones of color and grai'.size from very fine to micritic.
50 97.6-98.4 Limestone, light gray 7.5Y 7/1, with sand size darker "oo1;<:e"grains, micritic with sand size grains.
51 98.4-98.7 Limestone, grayish yellow 2.5Y 7/2, with darker sand size "oo'Uegrains, hard and dense, stylolite at 98.6.
52 98.7-99.2- Limestone, grayish yellow, 2.5Y 6/2, finely crystalline, hard arc:dense, bottom contact gradational.
53 99.2--101.2 Limestone, light gray 2.5Y 7/1, finely crystalline, "oolitic,"hard and dense, vuggy in places, stylolites at 99.55 and 99.70,latter with black "petroliferous" stain in solutional cavity.
54 T.D. 101.2
Lemon Lane Landfill Boring 2
Monroe County, Indiana Bloomingtor. Q'jac.Vang1eSW corner, SE^, SE*i, NE^, Sec. 31, T. 9 N., R. 1 W., Second Principal Meridian550 EL, 2680 SL, Sec. 31, T. 9 N., R. 1 W.Lat. 39° 10' 18" N., Long. 32° 33' 29" W.
Altitude (topographic) 885 corrected to 887Ground level 117.07Top inner casingTop outer casing 118.27Total depth 80.0
1 0-7.5 Red silty clay/gravel.
2 7.5-8.35 Limestone, m-.- •-• -"low 2.5Y 7/2, fine grain crystalline, ;
and dense, suvurji low amplitude stylolites; weathered an'stained; nearly vertical fracture 7.65-8.10.
1 r
8.35-11.1 Limestone, light gray 2.5Y 7/1, micritic or lithographic withfine crystalline areas, hard and dense, abundant stylolites(47± in 2.8') mostly with very fine spikes, a few with .10vertical range from side to side; possible weathered beddi ngplane at top; shaly streak at bottom.
11.1-13.1 Limestone, yellowish gray 2.5Y 6/1, very fine grain crystalline,few fossils, hard and dense, stylolitic and silty streaks intop .25.
13.1-19.6 Limestone, gray 5Y 6/1, fine to medium crystalline with minormicrite, hard and dense, abundant stylolites, very few fossils;CHERT (pinkish) light gray 5YR 8/1, with irregular black rinsand small dark spnts, fossiliferous at 13.95; solid brownishblack 10YR 3/1 at 16.0, 16.45-16.9 (very irregular mass);weathered and iron stained irregular vertical fracture 16.6-16.8
19.6-21.4 Limestone, gray 10Y 6/1 (glauconitic cast), micritic, silty, somesmall whole bivalve fossils and fenestrate bryozoans, hard anddense with abundant greenish silty streaks.
21.4-26.4 Limestone, gray 5Y 6/1, fine grain crystalline with some micritehard and dense, abundant stylolites, a few whole fossils; CHERT",irregular stringer, black 21.7 (.05 thick), 23.2 (.025 thick),irregular masses black, some with gray centers, 23.3-23.7,24.05-24.35 with streak of glauconite, medium gray with pinkishcream 24.4-24.5, p i n k i s h center with white rim~24.8 (.05 thicknodule), pinkish with gray rim 25.3-25.4, snail spots at 25.8,black irregular mass 26.05-26.15..
26.4-30.7 Limestone, light gray 5Y 7/1, fine grain crystalline, withnumerous glauconitic silty streaks, greenish gray 10GY 6/1, hardand dense but parts on silty streaks; CHERT, small lens ofblack (.025 thick) 27.85; large medium gray (.10 diameter) baTsat 28.45-28.55, irregular tabular mass, dark to light gray 29.4-29.5; slightly weathered, very irregular or rough verticalfracture 28.6-28.90.
Lemon Lane Landfill Boring 2
9 30.7-37.1 Limestone, light gray 5Y 7/2 to 5Y 7/1, fine to very fine graincrystalline, hard an^ dense (basal foot very tough 36.3-37.1),partially silicified solitary corals at 32.9-33.1, few stylo"Hteexcept at 33.1-34.1, high amplitude (3/4 ") stylolite at 34.9,few stylolites at 35.0-, calcit3 crystals in vugs 1"- indiameter at 36.7 and 36.8, bottom contact sharp and inclined;weathered stylolite at 36.16, possible weathered bedding planesbut lost owing to spin in core barrel; iron stained nearlyvertical irregular fracture 34.25-34.5; slightly weatheredsteeply inclined fracture 35.2-35.4; deeply weathered, ironstained irregular vertical fracture 35.7-36.1.
10 37.1-39.0 Limestone, o i . v t gray 2.5GY 6/1, micritic to very fine graincrystalline, hard and dense but with glauconitic silty streak-:-.
11 39.0-40.1 Limestone, as above, but with very abundant glauconitic siltystreaks, inclined bedding planes in bottom .5 of unit; possiblevertical fracture 39.5-39.7.
12 40.1-40.55- Shale or clay shale (mashed sample), light greenish gray 10GV
7/1 to 8/1, finely laminated in cart, soft, calcareous.
13 40.55--41.0 Limestone, light gray 7.5Y 7/1, microcrystalline, ve^y hard anddense, brittle; inclined fracture with glauconite on faces intop .10 of unit.
14 41.0-41.1- Shale or clay shale, non-calcareous to slightly calcareous, asabove, mashed sample.
15 41.1--41.6- Limestone, dark grayish yellow 2.5Y 5/2, lithographic, hard anddense, brittle; very irregular vertical fracture packed withoverlying clay shale.
16 41.6--44.0 Dolostone (very slight fizz) light gray 7.5Y 8/1, (white),micritic, earthy to chalky luster, some greenish glauconiticstreaks at all directions, medium hard.
17 44.0-52.8 Shale or clay shale, calcareous, as above, mashed up beyond allrecognition.
18 52.8-54.0 F i l l , silt or clay, calcareous iron stained chert in top of uni
19 54.0-61.6 Dolostone (slow fizz), grayish yellow 2.5Y 7/2 to lig h t gray 2.E8/1, micritic (very finely crystalline), dull to earthy luster,hard and porous, si ightlyharder and more calcareous zone 56.5-59.4 (macro-vuggy zone 57.0-58.0); nearly vertical slightlyweathered slickensided high angle fracture 55.4-55.6; crystallirlined vertical fracture (open) 57.7-58.3; high angle fracture58.4; irregular vertical calcite annealed fracture 58.4-59.3.
20 61.6-68.2 Shale and clay shale, light greenish gray 10GY 8/1, calcareous;mostly lost in coring.
Lemon Lane Landfi 1! Boring 2
21 68.2-68.55- Limestone, yellowish gray 2.5Y 6/1, microcrysta 11ine, hard anddense, top piece recored.
22 68.55--68.S5- F i l l , tan, siHy,.laminated, calcareous, oxidized in part.
23 68.65--70.2- Limestone, brownish gray 10YR 6/1, micritic to lithographic,hard and dense, brittle, some small vugs with c halky residue,whole fossils in bands; slightly iron stained vertical fracture68.65-68.80 into badly broken core; iron stained and c a l c i t ecoated high angle fractures 6°.4-69.5, 69.9-70.0 (lower par*.missing); TOW an^'e ^edd^c plane or fracture wHh -iron st.vn
and c a l c ^ t . - - _. ''".5; possible solution zo^e at 69.£ b..-'•_.badly broken core.
24 70.2--70.6- Limestone, pale yellow 2.5Y 8/3, micritic, earthy luster, hareand dense, porous towards base.
25 70.6--71.2- Limestone, grayish yellow 2.5Y 6/2, micritic or lithographic,hard and dense, brittle; steeply inclined vertical fracture irorstained with calcite 70.8- to 71.1- in badly broken core.
26 71.2--71.45- F i l l , s i l t or clay, pale yellow 2.5Y 8/4, calcareous.
27 71.45--71.65- Limestone, pale yellow 2.5Y 8/3, micritic, earthy luster, hardbut crumbles easily with hammer, iron stained.
28 71.65--73.0 CORE LOSS
29 73.0-73.9 Limestone, light gray 2.5Y 8/2, micritic, chalky to earthy lustehard and porous in places, hard and dense otherwise; calciteannealed irregular vertical fracture 73.0-73.9; top of unitiron stained as well as top .10 of fracture to suggest extremeweathering; vugs .10 across at 73.3 with chalky residue.
30 73.9-75.6 Limestone, grayish yellow 2.5Y 7/2, m i c r i t i c , d u l l luster, hardand dense, unit traversed by calcite filled vertical fracturefrom overlying unit, slight fetid odor at about 74.5-75.0.
31 75.6-75.8 day shale, light gray 2.5Y 7/1, soft, finely laminated.
32 75.8-76.4 Limestone, grayish yellow 2.5Y 7/2, micritic, silty, soft,earthy luster, porous in part, minute to small vucs.
33 76.4-79.5- Limestone, yellowish gray 2.5Y 6/1, micritic to microcrystal1inedull luster, hard and dense, trace fetid odor.
34 79.5--80.0 CORE LOSS
35 T.D. 80.0
Lemon Lane L a n d f i l l Boring 3
Monroe County, Indiana Bloomington, IndianaNear Center E4, SW*s, N'E*s, Sec. 31, T. Q N. , R. 1 W. , Second Principal1580 EL, 2050 NL, Sec. 31, T. 9.N., D. 1 W.Lat. 39° 10' 24.5" N. , Long. 32 33' 43" W.
Altitude (topographic) 872 corrected to 870Ground level 99.67Top inner casingTop outer casing 101.43Total depth 59.7
1 0-22.2 Red clayey silty residuum; split spoon 0-1.5, triconed to ??.
2 22.2-23.7 Dolostone (slow t- 'vz) pa'e yellow 5V 8/3, micritic, d u 1 1 1-hard and den^L, i... ic nt f i l l e d irregular vertical fracturestop part, badly broken core.
3 23.7-25.6 CAVE FILL, triconed
4 25.6-32.50 Dolostone, (slow fizz), light yellow 2.5Y 7/3, micritic, dull toearthy luster, hard and slightly porous; tabular CHERT, lightgray 7.5Y 8/1 with dark center 30.80-30.85; numerous small vugs29.3-29.45, 29.75-29.85, 30.55-30.75; basal 1.0 oxidized.
5 32.50-32.55 Dolostone (slow to fizz), pale yellow 2.5Y 8/4, oxidized, siltyand laminated, hard and dense; v^eathered.
6 32.55-34.85 Dolostone (slow to fizz), pale yellow 2.5Y 8/3, micritic, dullluster, hard, slightly porous; stylolite at 34.65; irregularvertical fracture iron stained and calcite coated, 32.55-34.85.
7 34.85-36.0 CORE LOSS
8 36.0-36.6 Limestone, grayish yellow 2.5Y 7/2, micritic to microcrystall ine,hard and dense, dull luster, pyrite stringer; CHERT, light gray10YR 8/1, with white rind, at base of unit 36.55-36.60; calcitefilled vertical fracture through unit, high angle racture 36.0-36.15.
9 36.6-38.7 Dolostone, light gray 2.5Y 8/2 to 7.5Y 8/1, micritic, dull toearthy luster, hard and dense, slightly porous in places, greencalcite eyes 37.1-37.6, some calcite filled tight nearly vertica'fractures.
10 38.7-38.9 Shale to limeshale, light greenish gray 10GY 7/1, poorlylaminated, calcareous.
11 38.9-43.6 CORE LOSS, piece of red day. Triconed 38.4-43.6.
12 43.6-44.3 Limestone, yellowish gray 2.5Y 6/1, micritic, dull luster, hardand dense, bottom k" shaly, same as top .05 of next lower unit,calcite annealed irregular horizontal fracture at 43.75.
Lemon Lane L a n d f i l l Boring 3
13 44.3-44.7- Limestone, yellowish brown 2.5Y 5/3, micritic, laminated, hardand dense, lower boundary transitional.
14 44.7--45.2 Limestone, yellowish gray 2.5Y 6/1, lithographic, hard and dense,small whole fossils in band at 44.9.
15 45.2-46.0 CORE LOSS, recored limestone piece .15 thick.
16 46.0-49.2- Limestone, grayish yellow brown 10VR 6/2, mic r i t i c l i t h o g r a p h i c .hard and dense (badly broken core with possible mislocated orout of sequence n^'^es); includes dull ^icritic limestone '•'places; vert ;. ' /re in top of unit .3+; w h i t i s h c halkyresidue in vugs towards base of lithographic unit.
17 49.2--*9.5 CORE LOSS
18 49.5-50.0 Limestone, light yellow 2.5Y 7/3, micritic, dull to earthyluster, hard but crumbles under hammer blow; top has calcitedeposition V thick.
19 50.0-52.30 Limestone, dolomitic (slow to fizz in top and bottom), grayishyellow 2.5Y 7/2, micritic, earthy luster, hard and dense.
20 50.30-52.7 Shale, clay shale, light gray 2.5Y 6/2, indistinct bedding,1 calcareous; includes .20 CORE LOSS.
21 52.7-53.8 Limestone, grayish yellow 2.5Y 7/2 to yellowish qray 2.5Y 6/1micritic to microcrvstaTline, hard and dense.
22 53.8-53.85 Clay, light gray 5Y 7/1, calcareous, with some very small vugs orcavities.
23 53.85-55.9 2.05 CORE LOSS IN GRAY CLAY CAVE FILL
24 55.9-58.85 Dolostone, grayish yellow 2.5Y 7/2, micritic, earthy luster, hard.porous, slightly vuggy 57.1-57.8.
25 58.85-59.0 Clay, light gray 2.5Y 7/1, laminated, hard when dry, calcareous.
26 59.0-59.7 CORE LOSS
27 T.D. 59.7
Lemon Lane Land^i 1! Boring 4
Monroe County, Indiana Bloomington QuadrangleNW corner, NE>a, SE'i, NE»s, Sec. 31, T. 9 N./R. 1 W. , Second Principal Mer^dian550 EL, 1420 ML, Sec. 31, T. 9 N., R. 1 W.Lat. 39° 10' 30.5" N., Long. 32° 33' 30' W.
Altitude (topographic) 8%Ground level 119.98Top inner casingTop outer casing 122.99Total depth 86.65
1 0-17.2 Augered to 16.4 to bedrock, then triconed to 17.2.
2 17.2-21.95 Limestone, ar?v; •• ''ow 2.5V 7/2, fine grain crystalline U,microcrystal 1 i i i u , rossi 1 iferous in part (fenestrate bryozoans'',hard and dense, small glauconite spots, small oxidized pyritegrains; CHERT mostly light gray 10YR 8/2 with l^aht and darkerareas, ball at 17.25-17.45 ball at 17.5-17.6. disc at 17.7-17.c.ball at 18.0-18.1, disc at 18.3-18.4, spot 18.6, edge of disc18.95-19.0, edge of disc 20.9-20.°5, edge of b a l l 21.05-21.15,trace of chert 21.30; stylolites common 19.0-19.7, 20.4-20.5;solution enlarged and iron stained stylolite, low angle, at18.10, iron stained stylolite at 19.0, weathered stylolite at20.45, 21.3.
3 21.95-25.20 Limestone, light gray 5Y 7/1, micritic, dull luster, fossili-ferous (bivalves and fenestrate bryozoans), large whole fossilsin places, parts unevenly readily by hammer, hard and dense,shaly streaks at top, 22.05, 22.3-22.35, 22.5, and glauconiticshaly streaks 22.55, 22.65, glauconitic shale bands at 24.80-24.85, 25.0-25.05 and streaked in limestone 25.10-25.20;CHERT, grayish white N 8/1 rims in part on gray N 5/1 and 6/1tabular discs, fossi1iferous, at 22.35-22.40, 22.6-22.7, 23.0(h" thick) 24.4-24.45; weathered bedding planes at 23.50.
4 25.20-26.15 Limestone, light gray 2.5Y 7/1, crystalline fine to medium withmicritic blobs, fossi1iferous, hard and dense; weathered lowangle break in silty streaks at 25.35, laminated f i l l (k"-)in bedding plane at 25.6, weathered bedding plane at bottorr.
5 26.15-29.25 Limestone, grayish yellow 2.5Y 7/2, fine crystalline to micro-crystalline, hard and dense, solitary corals with blacksilicious and clear calcite f i l l i n g at 27.9-28.3; CHER" lightgray 5YR 8/2 with black spots and partial very thin rim at26.65-26.7+; stylolites at 26.5, 26.55-26.60 (V amp) 26.70,26.75, 27.20-27.6 (numerous), 27.'9 (in top of corals); weatheredbedding plane (possibly stylolite) at 26.7, 27.5, and slightlysolutioned enlarged stylolite at 28.15 (in corals); steeplyinclined very rough fractures 27.75-28.15, inclined fracture28.95-29.1 slightly weathered with minor red mud stain, thinred mud fill at 20.25 on weathered bedding plane.
Lemon Lane L a n d f i l l Boring 4
6 29.25-33.9 Dolostone, light yellow orange 10YR 8/3 to pale yellow 2.5Y 8/3,very fine crystalline, dull *o earthy luster, hard and porous,dense in part, scattered fossil zones (fenestrate bryozoans),several calcite lenses or possible -^ossi1 casts, small ca'lcitecoral "eyes" 32.3-32.5, numerous small vugs in fossil zones,basal .05 of unit is light gray 2.5Y 8/1 and is only unweatheredpart, vertical calcite with pyrite in basal .05; very irregularnearly vertical fracture with iron stains but generally tic1".33.25-33.9; possible weathered a^c1 dissolved bedding p'ane30.3, 31.8.
7 33.9-34.0 Shale, l i g h t nr. -'• gray 10GY 7/1, laminated, olaucontic,
8 34.0-34.3 CORE LOSS
9 34.3-35.4 Limestone, gray 5Y 6/1, microcrystal1ine, dull luster, l a m i n a t ehard and dense with soft glauconitic shaly streaks, V shaleband at 34.40.
10 35.4-39.4 Dolostone (slow fizz), light gray (white) 7.5Y 8/1, very finegrain, with chalky to earthy luster, hard and dense, slightlyporous, numerous vertical glauconitic stringers, sone calcitei n f i l l i n g of breccia cavities, base of unit includes streaks or
shale from below; slightly weathered low angle smooth beddingplanes at 38.85 and 39.0.
11 39.4-40.6 Shale or clay shale, dolomitic, fizzes after penetration,greenish gray 10GV 6/1, laminated to massive nonlamainated :nmiddle part, soft (relatively intact core).
12 40.6-41.4 Dolostone (slow fizz), light gray 7.5Y 8/1, micritic, hard anddense, lower .5 intermixed with greenish gray 10GY 6/1 mudstorewith vertical contacts, units breaks easily with hammer.
13 41.4-42.6 Dolostone (slow fizz), light gray (white) 7.5Y 8/1, very finegrain, chalky luster, hard and dense; iron stained steeplyinclined fracture at 42.3-42.6.
14 42.6-43.6 Conglomerate, calcareous, light gray 7.5Y 8/1, dolomitic (s^owfizz) micritic matrix with micrite oebbles to .075 long,glauconitic pebbles or i n f i l l ings, calcite i n f i l l i n g of vugs;bottom .15 oxidized.
15 43.6-43.9 Limestone, pale yellow 7.5Y 8/2, micritic, chalky luster, hardand dense (note: top of this unit fits base of overlying unit-bottom of this unit broken by drilling).
16 43.9-44.0 Conglomerate, as above, smaller grains, on weathered irregularcontact with underlying unit, this unit badly weathered andiron stained.
Lemon Lane L a n d f i l 1 Boring 4
17 44.0-49.3 Limestone, dolomitic (slow fizz), pale yellow 2.5Y 8/3 to l i g h tyellow 2.5Y 7/3, very fine grain, in part laminated near top,and at 45.3-45.5; CHERT, irregular light colored horizonta1
mass at 45.7-45.8, very minute vugs in scatteredp laces, baseof unit horizontal; inclined fracture at 47.7-47.8, tan mudfilled void at 47.8-47.9 very calcareous and has very smallvugs in fill.
18 49.3-50.55 Limestone, grayish yellow 2.5Y 6/2, micritic to microcrysts11 -•-••hard and dense, glauconite band 1/16" at .05 above base of i:'.
19 50.55-52.50 Limestone, ^ ' ••/ 2.5Y 8/2, micritic, perhaps dolomitic(slow fizz), iidcu ar'd dense, base of unit shaly, glauconitk :••oxidized k" above and below.
20 52.50-53.0 Lime shale, dolomitic (slow fizz), light greenish gray 10GY II'..parts irregularly easily with hammer, slightly porous, bottomsoft; top V oxidized.
21 53.0-56.3 Shale, light yellow 2.5Y 7/4, bedding indistinct, mostly contortcalcareous, with whitish streaks.
22 56.3-58.05 Limestone, pale yellow 2.5Y 8/3, micritic, dull luster, hard anddense, but the minute vugs in places: solution enlarged incline-bedding planes 56.7-56.8, 56.9-57.15*.
23 58.05-59.65 Limestone, light gray 2.5Y 8/2, micritic, dull luster,hard anddense, vertical fracture with white calcite f i l l i n g 58.05-thinsto nil to 59.65; vuggy zone, interconnected with tan micriticinfilling 59.1-59.45, and broken at 59.35 but not weathered.
24 59.65-59.70 Shale, pale yellow, 2.5Y 8/3, with bright greenish streaks,finely laminated, soft, weathered shale, calcareous.
25 59.70-61.3 Limestone, light gray 2.5Y 7/1, micritic and sublithoaraoh^c,hard and dense, brittle (core badly broken owi-rg -Q cress'"., oftwo smooth vertical fractures and a fifth abuting verticalplane-open joints, with possible red clay infilling); crossedvertical fractures from top (broken core) to 60.6; unweatheredirregular steeply inclined fracture 60.9-61.15, solutionenlarged vertical fracture 61.15 to 61.30 with vuggy surface.
26 61.3-62.05 Limestone, yellowish gray 2.5Y 6/1, micritic, dull luster,hard and dense; irregular vertical to steeply sloping fracture,slightly weathered 61.3-61.85, curved fracture with dendrites,slightly weathered 61.85-62.05; top of unit vuggy by solutionfrom overlying porous zone (core pieces mixed and reversed inbox).
27 62.05-62.55 Limestone, pale yellow 2.5Y 8/3, micritic, dull to earthy luster,hard and dense.
Lemon Lane L a n d f i l l Boring 4
28 62.55-63.70 Limestone, grayish yellow 2.5Y 6/2, 1ithcc-a:-::, br-'ttle, hardand dense; high angle fractures 62.55-62.65 (left to rightslope), 62.70-62.85, 62.75-62.90, 63.0-63.15, 63.05-63.20,63.20-63.35 (right to left slope), with essent^ly a-; spacessolution etched; bottom contact weathered and oxidized.
29 63.70-64.55 Limestone, light gray (white) 7.5Y 8/1, mic r i t i c , silty, chalkyto earthy luster, hard and dense.
30 64.55-65.1 CORE LOSS
31 65.1-66.8 F i l l , s i l t s a'V •' .- . pale yellow 5Y 8/4, laminated, o x i d i , - - _on some la m i n a t loir.,, (mashed sample).
32 66.8-66.85 Limestone, d u l l yellowish brown 5Y 5/4, micritic, hard and dense.
3L '66.85-67.40 Limestone, breccia, dull yellowish brown, 5Y 5/4, mi c r i t i c , hardand dense; pieces in part annealed with calcite; appearspermeable; badly broken core-much loss of core.
34 67.40-68.15 Limestone, grayish yellow 5Y 7/2, micritic, silty, earthy "uste1",hard but breaks easily with hammer, porous, vuggy near top andbottom.
35 68.15-69.1 Limestone, grayish yellow 2.5Y 7/2, micritic, hard and dense,dull luster in top, brighter towards base.
36 69.1-70.40 Limestone, dolomitic,-grayish yellow 2.5Y 7/2, micritic, earthyluster, hard, vuggy :n part, porous in part, "st^kstein," lower.30 dense and very slow to fizz (dolostone).
37 70.40-70.6 Limestone or siltstone, light gray 2.5Y 8/1, poorly laminated,calcareous, soft in lower part.
38 70.6-70.75 Limestone, yellowish gray 2.5Y 5/1, micritic to microcrsytal1ine,hard and dense.
39 70.75-70.90 Shale, grayish yellow 2.5Y 6/2 dry, blackish when wet, laminated,soft (much core loss).
40 70.90-72.85 CORE LOSS in shale
41 72.85-74.1 Limestone, grayish yellow 2.5Y 6/2, micritic, hard and dense;unweathered nearly vertical fracture 73.4-74.1.
42 74.1-76.3 Limestone, grayish yellow 2.5Y 6/2, micritic, earthy luster,abundant minute vugs, hard and vuggy towards base; nearlyvertical fracture, 74.75-75.9; vertical fracture 75.45-75.7(both appear to be "drys" at right angles).
Lemon Lane Landfill Boring 4
43 76.3-77.65 VOID
44 77.65-78.35 Limestone, grayish yellow 2.5Y 7/2, micritic, earthy luster,hard and dense (top of unit recored).
45 78.35-78.40 Shale, dark brown 10YR 3/3, organic, laminated, soft.
46 78.40-79.80 Limestone, dolomitic (slow fizz), light gray 2.5Y 7/1, m i c r i t i c ,dull luster, hard and dense, calcite~"eyes" 79.5-79.S.
47 79.80-80.4 CORE LOSS .10 reddish fragment of overlying limestone.
£8 80.4-80.8 Limestone, l i g > : ; ji ay 2.5Y 8/1, micritic, dull luster, hardand dense.
49 80.8-82.55 Dolostone (slow to fizz) light gray 7.5Y 7/1 to gray N 6/1,micritic, silty porous, hard, parts irregularly with hammer Me1.-..
50 82.55-82.90- CORE LOSS AND BROKEN CORE.
51 82.90--83.7- Limestone, light gray 7.5Y 8/1, micritic, dolomitic (slow tofizz), hard and dense, some lighter soots, poss^e worn-burrows, in top.
52 83.7-84.05 CORE LOSS AND BROKEN PIECES.
53 84.05-84.25 VOID (driller)
54 84.25-84.55 Limestone, yellowish gray 2.5Y 6/1, micritic, finely laminated,very tough and dense; top of unit vuggy and solution modifiedwith black stain.
55 84.55-84.75 Shale, yellowish gray 2.5Y 4/1, (dark gray) finely laminated,hard but parts readily, calcareous.
56 84.75-85.05 Limestone, gray 5Y 5/1, micritic, dull luster, hard and dense.
57 85.05-85.35 Shale, yellowish gray 2.5Y 5/1 (dark gray) finely laminated,hard, with whole fossils, calcareous; low angle fracture at85.25-85.30.
58 85.35-85.80 Limestone, gray 5Y 5/1, micritic, dull luster, hard and dense.
59 85.80-86.0 Shale, yellowish gray 2.5Y 4/1 (dark gray) organic, finelylaminated, hard and dense, calcareous.
60 86.0-86.65 Limestone, yellowish gray 2.5Y 5/1 (dark gray) micritic, d u l lluster, hard and dense.
61 T.D. 86.65
APPENDIX LL-3
x !
APPENDIX LL-3
SUBSURFACE AND WELL LOGS. 1982-1983
WELL 1SWELL COLUMN
GEOLOGICCOLUMN D E S C R I P T I O N CAL IPER D I A M E T E R ( I N C H E S ) G A M M A R A Y COUNT ( M I N U T E S )
860 -t»«.*2' 1
MM'-, I
"* mOTCCTtVC i f*-1ITCEL CABINS Ul/ P
LOCKIN6 CA*-
850 -
840 -
8 3 0 -
«'0 •ONEHOCE -
82O -1/2" *VC CA3W«
2 1/2" PVC SCKCCN —
LIMESTONE. on»T TO murr,• O^T AMD SHALE, ««*t
eriAr, forrLIMESTONE, OKAY, torT tSHALE, OKAY. WATEMU-&O
T O T A L D t P T H soe M atLO* GHOUNU L
' 8 0 0 - -
790 -
z 780 --
8 4O 80 120 I6O ZOO
•LASIANO ft tOUCK
PC
WELL 1D
850 -
840 "
830 -
820 -
* 8 10 -D
<O
L 7 9 ° 'i~
Z
z 780 -0
•a
76O -
WELL COLUMN
sss *B-— i
.M.IV-J 1
F(J_ „
• 4 7 4 ' ,
"0 PROTECTIVE •
STEEL CASINO W/
LOCKING CAP
(•HAVEL
1/2' PVC SCHtEN i
1
1GROUT If
:Tti<iL
GEOLOGICCOLUMN
\_ s
^ — _^jr-_L--,— t^.
1 ^X-^ '^
g i 'i ' r
j^i^T
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' "---*
'.grr., •:;.;,. —V J , ~i .
i ^•! -ii-i .!]nn^_. •.,••li S^^
!Sg
DESCRIPTION
FILL
I [TAX" IB OWN
LIGHT CHAT. HAHD
SOFT AMD SHALE. «*<kf
LIMESTONE!. OKAY, IOFT ftSHALE, ORAT, W*Tt«U-S»p«)
LIMtSTO
03OH
HAHO
NE
CALIPER DIAMETER (INCHES) GAMMA RAY COUNT (MINUTES)
2 3 4 3 6 7 6 40 ' 80 1 20 160 200
- -
- --
1
- -
/~]/lr~^ MAttAHO* •OUCK
^£? •— *«•
WELL 1D
85O -
8 4 0 "
8 30 -
z 8 I 0 -15
O
o
^ 7 9 0 -
£.
z 780 -1o
J 7 70
WELL COLUMN
ass «•'— i
""•s'"l jFLL— —
• 47.4' .
1"0 PROTeCTIVE •
LOCH INS CAT
• ROUT
C.KAVE.LPACK
I/H" fVC SCMf EN
761 4'-,
TOTAL DFPTH . 93 i' |BELOW GROUND LEVEL '
GEOLOGICCOLUMN
'\ ' •. ' •
j -
i,1 ' ' ,=•-i • ,'i ':'i-:^
~rr- ;T
• ' 'IH f' I-
SS^^gg~rppq .^j,'_ J^,' 'i^^-
-,-• W--
S^^,--i;:r.
^^ '-; ',
KSjj ^ L _ ';
DESCRIPTION
FILL
; CAY* MOWNfiHAY.SOrT
LIGHT GRAY, MARO
LIMESTONE, ONAY TO IUFF,10PT AND SHALE. BRAY
OKAT, SOFTLIMESTONE. o«*r, IOFT *
L i r / L S T O
OO Cjft
Ht*D
I
1
NC
CALIPER DIAMETER (INCHES) GAMMA RAY COUNT (MINUTES)
2 3 4 5 6 7 8 40 • 8O 1 ZO 1 6 0 2 0
- -
I
' • : " " "
/ ~J/r~~7 • *U*HO > »ouc«t—y-T m mi^jc.
0
\
870-
DA
TU
MN
}
0>
0U
J J
? c
./> 820-o
D
£ 8K)~UJu
z
^ BOOo
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lu ^90-
/«o-
7 L>-
7bO-
WELL COLUMN
8«7 27' gr
3' POUT LAW) ™" •CEWCNT SEAL /
a'S ^RorecTivt — ^W/LOCKIHS CAP
*'<! lOREHOLt — »•
W/BENTONITE ,e»our
•4z o' — •-
4"0 6OBEHOLC fc.
,,,TT O T A l D E P T H - 105
BLLO* GHOUNO LE Vt L '
GEOLOGICCOLUMN
j,
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^ ?
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- J I - l '
'.-l' : \'_! j' I '
i . I :. r~ : r
DESCRIPTION
CL
C L A V J
CLAY :
CLAY :C L A Y ;
C L A Y
L IMES
860HY
8bO
:
: 830-
; 82O-
rTONF
bl'J
BOO
^'JO
780 '
f f O -
CALIPE
2 3 1
C-,
^
^~*^
WELL 2G A M M A RAY COUNT ( M I N U T E S )
60 200
WELL 3
690-
880 -
Dt-
O
=>
LJ
z
* 820-o
u BIO
BOO
790
7bO
760-
WELL COLUMN
M4S4'
BBI.IB'5' PORTLAND •-CCMCNT BCAL
B"« PROTtCTtVl-tTECL CAilM* «/LOCKIN* CAP
PORTLAND CEMENT-W/BCNTOHITCOROUT MJ-
762 i»"—
T O T A L DEPTHI 11*'BELOW GROUND LEV!
PI
jf
/••
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GEOLOGICCOLUMN
I ~~— ~~I
;^= j---^ j-
£rS-4^t?=^^ -
^f:'lr~C^'l' "Vl
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L=i_'.
j?=-f>'r
^r^
^^4;
^^
OESCRIPTION
CINDER FILL W/LIUESTONFRAtUENT*CLAY, HEP
BUFF, HARD
CLAY.BROWN JBUFP. MAUD
B A A Y , SOFT
BUFF, HARD
BROWM , SO^T
BROWN , HAHD
BSOWN .SOFTL IMES
BHOWN , SOI- T
CLAY. COLO -,
C R A Y - B R . , SOFTBR .HARD
4RAY-BR . SOF T
SHOWN, S O F T
G R A Y . SQf T
tTOHC
C R A Y . H A R D
BUFF-BR. . HARD
890-
070
860-
84CT
8^0-rONE
820
810
600-
760-
770-
760-
CALIPER DIAMETER (INCHES)
2 3
7
GAMMA RAY COUNT (MINUTES)
4 3 6 7 e 40 BO 120 160 20
{u
^5^"
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1987
L
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c^
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0
WELL 4S
880-
870
860
' 8bO-
•4C-
•" 84O0
83O
f.p-'Qj
<3
UJ
J BIO
60O-
790-
/eo
7?0
760
WELL COLUMN
SBT.4»'
BB4.U — p
W/LOCKINfl CAP
QROUT *
'i """""•-
•" 0 •OMCHOLC— •
fn
_==
GEOLOGIC
COLUMN
sftS'S'JilSg
r ' i•H;:T^
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: , ; .
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D E S C R I P T I O N
CLAY, RED
BUFF, NA10
CL AY. SHOWN '
BUFF, H A R D
G K A Y . H110
BUC
F. H A R D
CLAV, BROWN
• urr -BR H A R D
FILLED
9RAT.NAIIO. TRACE BR
C L A Y . LT B R O W N q
C.OI DEN Ht IGE . SOF T
t iR , H A R D
C L A Y HRBR M A N O
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-it
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(•CL)-
/60-
C A L I P E R U I A M E T E R ( I N C H E S ) GAM MA RAY C O U N T ( M I N U T E S )
2 i 4 5 6 r 8 4O 60 li>u 160 20O
~ ^
- - 1
^1
^^
1-
~^—
t.
^P>
r^
^=>
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1
.
'
" •
^£ ".X.
}4
-A HO * BOUCKHIM. * C
3 4 5 6 7 4O 80 120 160 200
40 80 120 160 200
C A L 1 P E R D IAMETER ( I N C H E S ) GAMMA RAY COUNT ( M I N U T E S )
?U I6O 2UU
FINE GRAINED.BUFF,UODCMATEI.Y HANDSOME L M C B T , F R A C T U R EAT 31, DRY
* V»CL L M A T ! R I A L
ADDIU 1/6/88
PER W L 5 T I N O
MOUOE AUTHOR
I Z A T I O N
WELL 8S
850 '
Dt-<0
O
^
L. 80° ~UJ
Z
z 790-0
j
WELL COLUMN
•3340
4"* MOTlCTlve— '
• TLCL CASIM
W/LOCKIMfl CAP
• ROUT *
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g ' "pVC CASINO —
,.Z S C R t E N
GEOLOGICCOLUMN
— —
-is-gg r
,' 1 .'-r^
-?-17'.-~
i r i .
•',' "•-,-'•' v
Xi^ptj
j ^Lu j
T1', : • ' ; - .—
DESCRIPTION
HARD
««« LIMES
OK I,. HO. SULFUR ODO.,
ODOR
W A T E R ( . 3 gpn)G R A T . 3 W T »ND SHALE, O R A Y
w A T t R d i - 20 OP" 1
85O-
84O-
8 30-
TON E820-
810-
8C>0
790
CALIPER DIAMETER ( INCHES) G A M M A RAY COUNT ( M I N U T E S )
2 3 4 5 6 7 e 10 80 i?u 160 200
'
£{
. _
•-
— --
ly/—7 »uii*Mo t toocx</ j iiimiiiiti. re
6 40 80 120 160 200
50*
UFP-BR. UODLRATELY HARD
•UFP-8RAT.SOFT ftSHALE.GRA
8 40 8O 120 160 ZOO
APPENDIX LL-4
F TJ5
X
APPENDIX LL-4
SUBSURFACE AND WELL LOGS, 1987
/. -JZr—7 ILAI LAND I iOUCK~2^ -7^ INOINEiRS, P.O.
SOIL DATA
u
1
Q.
0
1 '
. 1 ,'
su
SA
MP
LE
S
oz
5
1
—
••'
—
—
—
RE
CO
VE
RY (F
T)
.65
l.F'i
,.-,;,
_
3
Z
It
7
10
-—
__.
ROCK DATA
OZ
z=)cr
-
—
--
—
._._
1
Xod:u.
~
~TT<
1 0 . H
1 j.U
o1-
—
•-•
7n <
l '. .
7 7 . 1
%
RE
CO
VE
RY
-
F, V
' <V
•)•;•
o01C
~
t-
5
UJ
•1
—
—
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
0-0. /5 ASPHALT, GRAVCL
lidhl (ir.iy ( ' / ! ) ! t r ace r.HAVn i i> t n , » (,1 tponn ,il.i t mot I If. 1* O. f .S ' .
;.:r • - ii.. • • T L A - , '.i i: , , > . • ! i-.,-, [ / / : 0 , ../i ;.. ' . '-]• .1, i i l l I - - - , . n,1 • • -o ,1 . , - t i l ! , (|- , .
qr.idinq tn ret ( r >/ f> ) n/ ' ', f r jqrr-.*-nf . , rnnf *• d.:'i;i i, t .Spoon refuel r t t 7 . 7 5 ' .
N!i 01 130RIN''..
7. . • * • , ' - H,.n' HHiMNL , 1 i -jilt (|i .iv , { ~/l ) 1 i ' i . -,-- , -.1 • 1 I in,- , MI Lr .'irh: i f . . - ' . : 1 1 r ,1( ) i ." '"t . .
5 .0 ' CHERT odul , bUc and oi-rtmji-
5.V CHERT odul , blac BR7N5.9 r j ' CHER I nodu e6 .6 ' -21 .8 ' IHESTONE, 1 qht o l i v e nr f ly 5ly
(1)Y 6 /1 ) fin -medium gro ned
16 .6 ' -16 .9 ' CHERT nudulca, whi te
or
u.
CC
i
o ^
si "o °
Iv.'i1— '
1r
L1^r'"""^._L
i
11i1 '
UJ _J
=c o
n
Dt»rE ELeu«Tinu 886.35 DATE 10/16/87
(• OF C A S N G Fl EVATION 88! j-12 ( i nne r ) 865.3". (outer)
Pf?
PR
LO
CL
n.lFTT 1 I T I F Supplemental
n.iFrr WIIURFH 117.36rarinM Lemon Lane Landfil l
ASS FIFO nr JLJOlFCKrO H
GAMMA RAY
b.
ZO
J
(85. 3'
iHO. V
B / 0 . 3
RANGF 10 TIME CONSTANT 10
C O U N T S /MINUTF
IO 2O 3'J «0 50 GO fO BO 90
nO t20
r-i — i-
— i — i — i — i -i i
-
/ ;O A T F 9/16/fl7
y NEC
CALIPEK
IDLE DiAML FEf<
(INCHES!
*> 8 (0
-
-
-
1- 1DA1F S/ lb/B/
FEHMtAB L I T Y
0 o
to
r)
O
0/rE 9 / 1 5 / 8 7 .
BOHING/CORING/WELI. NO . . '
N O T E S
witl i 3" ba r re l . fceomed out to 8"to 13. t ' iei f i -b/8" Mr.-l c-iain,;,coffi i-nt cd in p] ,,( (-.
9 / 1 1 / 8 / COWLI) 1 r oin 11.0' tn Vi .u ' ^ - : i l i 1,"h.ir r i-l .
!, u ' -• 1 .M / l ' . / - ' . . ' I Dr. ' ! [ ' • r,-. : • _ , _ , ' - • • . , ' .
I - '.•:•:.' • • . • ! . . • • c : r . ' ' . • . , . ] , , ; , . . , ;
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» • . . : ! ' - - •• IN.I , -..-,,,,) - .. 7] . ' • .
"" ' • ' " 1 ' - r i •, i n r ] ,'l . V ",i. ; ' . f,, ;,;,..•
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[ ' " . / . r, ' - ," 1 . V 1 .,:, | , , . • • • • • - / ' "... '
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<'/?^. '»; A H , ! - - . ! . . - n . M i r i ,, 1.7 . , . •' ) / ? ' ) . 'H / A. ' - ] . • , ! ( • • i ' n - 1 , ' In >J . [!' I - . , , - I ,,. ,
1 '.- /'i.'H; [ > • • : •• } .. | ' . - [ 1 i ' • . . - ( ] ,-,.. 11 "A | i ,
r J ' i ! ,• • ' • .u ! in '--, I ,'L :
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[ i f -1 1 F f ! ( ] - '.i-,1n... P,., .,.- T,*
z J# J ILAIIANO 4 IOOCK"7? ~f IN9INIERS, P.C.
SOIL DATA
P
DE
PT
H
20
30
V.
SU
1C
SA
MP
LE
S
SA
MP
LE
N
O
_..
RE
CO
VE
RY (F
T.)
UJ
t
ROCK
0z
z
tr
—
4
2
iu.
?7 .n
oH
''1 .
DATA
cr
oUJa:
£
V,
QOcr
-
RA
TE
(MIN
/FT
I
—
—
—
—
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
17.6 ' 4 17.8 ' S tyo l l t e BR7N18.25 -18 .5 ' L IMESTONF, , is obovc, l lqht gr . iy (N?)
\<i. 1' ClirST mirililfS, bl.lck nnd nhilc. 1 i mr',t>.ne
20 .3 ' - 20.75' s l ight ly laminatedmsf
21.3' CHERT nodule, BlacV21.8' - 21.0' LIMESTONE, medium light gray (NO)
2 2 . 6 ' - 2 2 . 7 ' L1MLSTONC, very light g ray (N8) msl's
medium q,,,inrd. c'
? < 4 . h ' CIILI'l nr.d.jli"'., ,,li:l|.".in,'l 1 . 1 . i< I,•").(!'>' !'.' i I t .Jtn-., i- I...IHII.- ,.• '? r>., ! 1 C r i r , : . i d en 1 umr... 1 -.:5.r)' t :M!HI , b l ^ c k ,in<i ,,r-..-,(r. / , i , - - ! . " ' r f
rr..'. ' i «•.',•: i , r . . r .3i ~ i.i... r . • ; : ••
7 B . 7 1 CIILH1 -hitc anil I.IH,-'.
c. l lc i tC 'ill, y e l l o w i s h . j r . l y ( ' .V H/l ) ...•:> t i n ^ ^
iji .1 i nf d .
31 .7 ' -31. r,' MML51UNL, me'JIun l ight, n r ^ y ( [:f. ) f i n , .
3 1 . 7 ' t gi^uconitr cpcci throughout l^min.ir
31. U' imall viiij-,
31 .T I ron itaioe.l 1 j.r.in.ie
v e r y f i l l ' - gi .lined, ea r thy , gl Hue on : t .- - RR7N,f i 1 Ipil f r ,i,:l uic 3'i.U1 '3 r>. 1 ' 'n'
SIIALE.3 8 . 0 ' - 3 9 . 2 ' DOLOSIONE, brecciatod, light t i lue/nray
I5B 7 / 1 )
39 .7 ' -39 .5 ' L IMESTONE, light o l i ve gray, (5Y (,/ 1 )\ f ine-medium grained.
RO
CK
FE
AT
UR
ES
^'
BRZN
GE
OLC
GIC
CO
LU
MN
1
-1— p-
Ji
1
V-, l '
r--1
L_L
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T"
pi- •
1
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I" '
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LC
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UM
N
1
prai-F n ru/vyinu 885.35 . DATF 10/16/87P OF CAS NO ELEVATION 8^.35 outer 885.12 Inner
PR
PR
LO
CL
u.
0
^-
iji
nr,5 . 3
KIM 3
n-iS.i
BiO. 3
n.lFTT TITI F Supplemental Hydrogeologtc Investigation
rVFOT N';MPF" 112.36
CATION Lemon Lane Landfill
ASSIF1FD RY JLJ rHFTKFn ay "EC
GAMMA RAY
BAIJI-.r 10 TIMF CONSTANT '°
COUNIS/MINUTt
~ _, no: -j)
X
r :./ -/ :j
\\./
\/
;-f
\
,/f
v."U 120 (30 140 Nv
1 1 — 1 — h \-__••-
' i • i i iDATF 9/ IW87
CALIPER
"OLE DIAMETER
(INCHES)
6 • 10
-
-
"
;
' ' 'OATf3 / lG /87__ .
PERMEABLITY
o
i-VIUJ
Oz
u
*
02
IS)
•*
.MTEO/ 15/87
nofi;wG/coRiNG/wFi t nn
NOTES
M.S. mud stained
z. jaf r MAS UNO » BOUCKjf ~f mOINIIBS, P.C.
SOIL DATA
u.
IHd
O
*5
so
•15
f 0
Si1C
SA
MP
LE
S
SA
MP
LE
N
O
—
—
--
—
—
RE
CO
VE
RY
(F
T)
—
=j_iSz
—
- -
—
—
—
—
—
DFACE ELEVATION
P OF CASINC, FLEW
ROCK
bz
zo(t
b
--
-—
-<i
XO(ru.
11. C
z55.
O>
55.
r
—
•—
f/i.O
-.
-.—
UA1A
K
-»0
Ua
74\
- - -
74^
-
oOre
;::
—
——
— -—
RA
TE
(MIN
/FT
)
-/_—
—
—
—
—
—
—
—
—— '
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
39.1)' - < t l . O ' No recnvpry, lo«,t. COM-
''tl.O1 L IMFSTONE, light o l i ve g roy (Sf f./i) ^
M.91 - 4 3 . 2 ' LIMfStONE;' IjghL gray (N8) brecciatedwith glauconlte (nHthi f ied f i l l ing, chalky luster
W.I'-M.l' DOLOSTONE, light olive gray (5Y 6/1)
fine grained "^rd
fi4 ? ' -id 7 ' CLAY Cdvl tv f i l l ) vei'v nal e oranoc\ 1 IU TK C/^ J /i f f c .7 1 - 49.1' OOLOSTONE, light gray ( N 7 ) f inegrainpd
^ 4 . 6 ' - ' tO .O ' mnr- poroin m^ f
1*6. /V f j l c i t P "r -y i -1 , " l ^ p j r r y c . l lc i t f )
W. i ' -'• 7 . C . 1 '-IT c |n , r nir.
'i'J.1 ' - l. lJ.f i1 MM— ,I:iN[, li,(ln. < . l : v - I . - .1V C-.V t . / l )diMir.i-. f i n * * i"-.):i.-:lSO.O '•' v I'll i to
liU.IV -M . '* ' I I M r S i i i N l , y r l l o« ; ^h qr v, ( jY H / l )w i th ion.- C . i l i i t " :nf l l l ir . i i-., f :n^- r i . . , l - : ,,-n r jr . , i r- .-<1
1,1 .tt '-M,' Nn r . - . - . i v . ' r y
(5Y B / l ) f lnc-n^d ium rjr^inpd
iS.O-5S.r,0' LIMhSlONL, light gray ( N7 ) f i in- gr.iinjmt
55.6-^7.0 ' S U T S T O N r , nw'ditim l ight grL iy { Nfi ) rnsf
rouyh t.f - turc
( 10YR B/f.)
S 7 . 8 1 - li^.O1 L IHFSTONF, p.i'li- y e l l o w i s h hro»n UHZN110YR b/Z) Mne grnincd denst;
58. 2 ' som?, more |»u uui
inf Il l lnqs
885.35 nATF 10/16/87
TION 885.12 inner 885.35 outer 10/16/87
RO
CK
FE
AT
UR
ES
GE
OLO
GIC
CO
LU
MN
WE
LL
}~7 . "
~^] 'X N.
-X "• ^
^;i
iii
ij.r
" r1_ i- ,""i •
-r-1-
J
PRn.lFCT TITI F Supplemental Hydroqeoloqf c Investigation
pRn.iFrT WIIUBFO 112.36
I nrATinw Lemon Lane Landfill
CL
1 C
OL
UM
N
ELE
VA
TIO
N (F
T)
8"l0.3
1
S!5.1
U30.J
BJ5.3
v .
DATE
iRSIFIFD HY -"-J r-HFPkFn RY NEC
GAMMA RAY
COUNTS/MINUTE
in ?o so 40 30 to 70 ao 40
/
1- \r \
- l«
_,
\\
/\\
- HO 120 IMJ 140
:-
1(\
: V0/16/87
CALIPER
(OLE OIAME TER
[INCHES)
c a 10
-
-
-
-
-
DA
\
-
-
)
Fo/ir, /87
PERMEABILITY
ozi~UJ
DATE
fj
g
i-i/i
t-*
dzt-10Ul
9/1S/B7
RORINS/COR1NG/WEL1 NO MW~IO
<?HFfT 3 OF 5
NOTES
M.S. mud stained
Run *5 Barrel is overpact^O dun- ti- i tn.in upper part of run.
z 10 t HASLANO <V iOOCK~3r~~f BWINIIRS, P.C.
SOIL DATA
T1-O.
O
80
.85
SL
Tr
SA
MP
LE
S
RFAC
P 01
SA
MP
LE
N
O
E ElCAS
RE
CO
VE
RY
(FT
)
.EVAING F
13
i
z
—
—
ION
LEVA
ROCK
0z
z
(E
7 '
id
TION
I0OL
69
—
83
88S
0t-
83
— •
--
_
-••
97
.12
DATA
crbj
6
IT
—
itm
-
—
--
93X
0
tr
^?
—
—
—
—
—
1OAT
n,er 8
RA
TE
(M
IN/F
T!
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL/ROCK CLASSIFICATION
to medium grained, dense ms
6<t.*' same as above, wi th some c a l c f t e in f i l l ings
6y.O- 7 1 . 2 ' UMLMUNL', l ight o l i ve qrjy { 5Y (,/ 1 } „f Inr-rncdi un q; ,i1 neil , dcn:,e
? 1 . 2 ' - 7 7 . 7 S ' M i inSTOfJF , r.lli|hi.ly i ,ili , ir .-..u-, , , . l i V Mqray ( 5Y k/\ ) fore i •, ruuuh
/ 2 . 2 S ' - 7 2 . 3 S ' L IMC^ .TONE, hUrk fin., nf . i iner l
7? . Vi' -7 f ) .0 ' I.IM1.51UNL, o l i v e qr.iy ( '.-Y ' , / ] ) I j nn
/ ' i . 0 ' - 7 ' * . 1 ' L l M C ^ I O U r , b lnrk f i n e ijf .1 i MM,)
7 f i . O ' - / 7 . 2 ' LIMLblUNL, Hqht oMve qruy C..Y f../1)f ini-mort ium grained
77. ' ' -78.0 ' L1MESIONL, medium qr.iy ( N ^ ) t i no
78.0 ' -78 . '3 1 L IMESTONE, light o l i ve gr.iy ( !)Y b/1)npdi um grd i nnd78.3 ' -80 .9 ' LIHFSIONF, lighl ,r^y (N7) BRZNA
IS.*' vuggy
c
J0.1J'-83 I No recovery
i2.82'-83.95' (Includes 0.18' Recorei DOL05TONEwdlum Hght gray (N6) fine grained; calc i tc f i l l edit 83.3 ' and 83. 41
B5.35 outer 10/16/87
RO
CK
F
EA
TU
RE
S
/
n
GE
OL
OG
IC
CO
LU
MN
WE
LL
'
1
T — 1
1
-.
-nil ;.j- - p
1 rL
1 -E
1 '" tF
-~
1 - '1
C
1 >-
1 ?i
^ \ J i
•v ^v ; =
'" P
PROJECT TITLE Supplemental Hydrogeologic Invest 1 gallon
PRnjFCT NIIMRFB 112.36
LOCATION Lemon Lane Landfill
Cl ASSIFIFD BY JLJ ruprkm BY NEC
CO
LU
MN
EL
EV
AT
ION IF
T)
\
'?n v
• 111.3'j
i'• 810 3
I 805 .
')
5j 800.3
DATE
GAMMA RAY
RANftF 10 TIMF rON5TANT '°
COUNTS/MINUTE
IO 20 SO 40 50 (0 70 BO to
)
/_
\: /(._~- -^. >
/\
- IK) l?0
, - - - • • •
. - - - - "
\
;'.
-
f '.
/
_ ItO IZO I3O "-^^
— 1 — 1 — h ---.
' i'' i i9/16/87
CALIPER
HOLE OIAMETF.R
(INCHES)
C s 10
:
\-
-
-
DA
-
\
-
\
1 '- 'F9/16/87
PERMEABILITY
(
t~
ui-
F
O
X
OAT
O
1-
UJi-
*
E
•«
O
_
ro
O
1-V)
i-
If
-"
U,
BORING/tORING/WFl 1 NO MW~ IU
NOTES
M.S. mud stained
-
-
-
* Irsts performed at 10 |isl.
Z)A> I ilAtUNO » IOUCK
~jy~) INOINIIRS, P.C.
SOIL DATA
u.
IK-o.
90
'j'j
.100
SLTC
1
SA
MP
LE
S
1 S
AM
PL
E N
O.
~
—
ISEC
OVER
Y IF
TI
—
—
—
—
—
UJIS__1$•z
—
—
—
—
ROCK
oz
z
tr
—
—
—
—
—
—
Xooru.
—
--
oh-
_
D A T A
LJ
O<_>a:
^
- —
—
aott
—
—
——
—
RA
TE
(MIN
/FT
)
—
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
85.5'-85.6' LIMESTONF, medium dark gary (til.)f ine grained85.6-92.4 ' LIMESTONE, dark gray (N3) thin beddebfine grained
90/8'-90.0' "honeycombed" feather ing msf
'.I?.!*' - ^ 5 . 7 ' l l r r S T O f i r , medium qrjy { [ ! ' , ) t ] noc r y i t j l 1 inc
<I5.7 ' -97 .0 ' No recovery
97.0 cm or CORING'Jb.l' lotol depth measured
IROC
K FE
ATUR
ES
»."~
GE
OL
OG
ICC
OL
UM
N
^ |
11
1
1
|
]
11 ,
1
• v _.
1
j W
EL
L|
C
OL
UM
N
1$'l\\
1
r, nr r«<;iur. n FVATION885. 12 inner 885. 35 outer 10/16/87
PR
PR
LO
CL
IELE
VATI
ON
(FT
)
795. 3
790 . 3
788.3
OJFCT TITLF Supplemental Hydrogeologfc Investfgaclon
n.lFt-T NIIMRFR "2.36
PATinw Lemon Lane Landfi l l
A.SSIFIFf) HY JLJ nwcrKFD BY NEC
GAMMA RAY
RANftF '0 TIMF CONSTANT 10
COUNTS/MINUTE
10 20 30 40 50 £0 TO BO 90
<c- 1 -
\ -
} :, /
,x'
/
; ; ;
: \\
-
-
i i i i i i i i .OATF 9/16/87
CALIPER
"OLE DIAMETER
(INCHES)
6 • IO
-
-
-
-
-
-
-
-
-
_
-
-
-
-
-
-
1 1 .OATF 9/16/67
PERMEABILITY
0zt-Wllu<-*
CM
i
t-
V)
".
K>
cf
£".11
DATE 9/1 5/67
BORING/CORING/WELL NO MW~IU
NOTES
M.S. mud stained
* lests performed at 10 ps l .
z IO> * UASLAND 4 IOUCK~JP~J INOIN1IW. P.C.
SO DATA
In.
0
. s
10
SIT(
SA
MP
LE
S
SA
MP
LE
N
O
~
RE
CO
VE
RY (
FT
)
—
UJ13
S
—
—
—
RFACE ELEVATION
IP OF CASING ELEVi
ROCK DATA
Oz
2
CE
OaLL
—
—
—
o
—
--
—
—
-
TION 888.76
%
SECO
VERY
-
ooa:
5?
—
RA
TE
(MIN
/FT
)
___
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
0-9.75 CLAY, red silly
microcryslalline soft at 13 0'
ROCK
FEA
TURE
S
GE
OL
OG
ICC
OL
UM
N
- -
r
1_
I
T
I
I
I
I
I
|
I
I
WE
LL
CO
LU
MN
| 1
DATF 10/16/87
10/16/87
PROJECT TIT1 F Supplemental Hydrogeologlc Investigation
PROJFCT NUMHFR 112-36
t or/ATION Lemon Lane Landfi l l
CLASSIFIED BY Ju rurrttfn HY NEC
GAMMA RAY
ELE
VA
TIO
N
(FT
)
186.3
tSl .1
37 f> . l
1
871.3
DATE
RANGE '0 TIMF CONSTANT '0
COUNTS/MINUTE
IO 20 50 40 3O SO TO 80 10
-
-
-
MO l?o
1 1 •
,-'
\
/ :-.^
/i i i i \
11/23/87
CALIPER
HOLE DIAMETER
(INCHES)
1 4 C
1
-
-
-
-
-
-
-
1 1
-
-
~
-
-
nATFlf/14/87
PERMEABILITY
(5
tftUJ
~|
bzi-
*
fO
07.
UJ
DATE?/!^/.
BORINGytORING/wFI 1 NO MW II
NOTES
9/2/87 Air rotary drilled with tnconeroller bit via a GardnerDenver 1 5- W drill rig to15 0'. Set 6-5/8' steel
9/3/87 Air rotary drilled with 5-5/8'trlcone roller bit (bore holesize 6-1/6') developed with
9/9/87 Pack* tatted.107l4/87Gamm ray logged with Keck
Qamm ray loggert i723/87C«lipe lasted *itn Keck
canp loggec.
-
87* Test j per formed <it. 10 p s f .
/ }# J BIAILAND * BOUCK
~7r~T INOINIIRS, P.O.
SOIL DATA
K-
I
Q.
Jr)
m
YJ
, 1*0SI
T C
SA
MP
LE
S
SA
MP
LE
NO
.
—
—
RE
CO
VE
RY (F
T)
UJn
sz
—
—
RFACE ELEVATION
ROCK OATA
oz
zutr
I0a:u.
—
—
—
o
—
tru•>0
a
-
_ _ _
-
P nr ri^iur. Fi FVATinw 888-76
0ocr
--
--
—
—
—
it\z5UJ
a
—
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL/DOCK CLASSIFICATION
18.75'-20.5' LIMESTONE, light gray (N7)race glauconite. toiler at 19.5
20 5' 22 0' LIMESTONE medium gray (NS)glauconite
22.0'-27.5' LIMESTONE, medium gray (N5)with some light olive gray (5Y 6/1) mediumcrystalline, lossi l i ferous
27.5 ' -30 0' L IMESTONE, medium uiay (N5).lossi l i ferous with glauconite specs, with daikgray (N3) CHERT at 28 25 ' -28 V
300'-31.0' LIMESTONE, light olive ar.iy C>Y6/1) with glauconile
31.0' 32.75' LIMESTONE, medium daik qrny(N4), soil, l i ace lossi ls
32.75'-35 S1 LIMESTONE, medium grny (N5).trace dark gray (N3) CHERT
3S.5--37.S1 LIMESTONE, light olive gray (5Y6/1) hard. honeycombed? weather ing at36.5'?
39.0'-40.5' SHALE, or clay, greenish gray(5GY 6/1) soil
RO
CK
F
EA
TU
RE
S
IGE
OL
OG
ICC
OL
UM
N
I
I
I
II
I
II
|
LI
^-
^1
$1i
, 11 ,_
1
|i
il
i1
- ' - ' -
WE
LL
CO
LU
MN
nATF 10/16/8710/16/87
PROJECT TlTl F Supplemental Hydrogeoloolc Investigation
PRnjFCT MIIURFR 112.36
1 OCATION Lemon Lane Landfill
Cl A5<;iFiFn BV Ju . CHFCKFn RY NEC
GAMMA RAY
EL
EV
AT
ION
(FT
)
B66.3
101.3
fllC.)
,1.3
8iiC.3
DATE
RANC.F '0 TIMF CONSTANT '0
COUNTS/MINUTE
IO 20 JO «0 SO CO TO BO 40
\
\
1
-
.
.-'":" -
\
\
/
/
/
\
11/23/87
/
-
CALIPER
HOLE DIAMETER(INCHES:
1 4 C
-
-
:
-
-
-
-
-
-
."-
-
-
DATF 10/11/87-
PERMEABILITY
i-
tn
l-
n0zK-
trtUJ
t-*
n4TP9/'J,9/4/
nnRiNn^npiufi/wFi i NO MW II
^HFFT 2 Qp 5
NOTES
-
-
-
17* T e s t s performed Jt_ 10 [is!
/~ffi J UASIAND * iOUCK— "g' —T INOINEIK, P.C.
SOIL DATA
u.
I
aUJo
•
Si
T C
VI
1/1
SA
MP
LE
NO
.
- -
RE
CO
VE
RY (F
TI
-•-
UJ
32
—
RFACE ELEVATION
)P OF CASING ELEW
ROCK OAIA
OZ
z
—
E
—
—
—
3oau.
—
—
—
o
—
—
—
—
rr
auta:
- -
—
—
oOcr
$••
—
— -
—
—
—
HA
TE
IMIN
/FT
)
—
-
—
SUBSURFACE LOG
SOIL /ROCK DESCRIPTION
SOIL /HOCK CLASSIFICATION
40.5'-41.Sf LIMESTONE, light olive gray (5Y6/1) medium grained, hard41.5'-46' LIMESTONE, medium dark grny|N4) slight greenish tinge
46.0'-65.5' DOLOSTONE. medium dark gray(N4). solt at 55 O1 and 59 0'
TION 888.76 10/16/87
ROCX
FE
ATU
RE
S
GE
OLO
GIC
CO
LUM
N
A
|
1
T1
— P
Ji_
— -
—
-^• \
\
WE
LL
CO
LUM
N
Pnn.iFTT TITl F Suppl«inental Hydrogeologtc Investigation
PR
LO
CL
n.rFPT KlilURFR 112.36
PAT ION Lemon Lane Landfill
ASSiriFn BY JI-J rMFTKFn BY NEC
GAMMA RAY
ELE
VA
TIO
N (F
T)
811. 3
Hlh. !
031 .(
8J6.
DATE
BANP.F TIUF mN^TANr
C O U N T S / M I N U T E
IO 20 30 4O 9O CO TO IO 90
J/
\.^X
^Vno *
L ' ^i
[_ -_ _ . - - - '
/
v\
• •>
/'/
j1
: I\)/\
I'O 120 ISO I4O X
— 1 1 | | S— — -_
~" '
'
.'
11/23/87
CALIPER
IOLE DIAMETER(INCHES)
t 1 C
C
-
-
-
^
-
-
>-
'--
-
\-
IRATE 10/11/87
PERMEABILITY
CM
ih-
Ult-
~|
\
e
o
rO
bzt-
*
OATFJ/9J_?/.1
nOR'N^A'nR|NR/wr( i NO
NOTES
-
-
87* Tests performed at 10 psi.
zf-J& r HAtUND . 10UCK•• r —f INOINK K, P.O.
SOIL DATA
T
Q.LU
70
•
•85SL
TC
SA
MP
LES
SA
MP
LE
NO
.
UJ13
§
Z
—
—
—
ROCK D A T A
O
Z
(C
—
—
2Orru
O
- -
orArr n rviTinu 886.3
%
RE
CO
VE
RY
—
— -
-
o0d.
—
—
__.
RA
TE (
MIN
/FT
)
7—
—
— -
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL/ROCK CLASSIf lCAT H
>
65.S'-77.5' LIMESTONE, light olive gray (5Y6/1) hard, with reddish mud at 700'
77 5-90.0' LIMESTONE, brownish gray (SYR4/1) soil at 82.5' and 87.5' grading grayerat 65.0' with t r a c e black (N1) limey shale
RO
CK
FEA
TUR
ES
IGE
OLO
GIC
CO
LUM
N
\ . Y
\
i
II
I
I
^Tl
P— i — i-lI
I
I-i-1 —
VI
11
11
WE
LL
CO
LUM
N
HATr 10/16/87
D or rAQiur-. n FvoTinw 888.76 10/16/87
PROJECT TIT
PROJECT Null
F Supplemental Hydroqeolqtc Investigation
BFR 112.36
i nr-ATiniM Lemon Lane Landfill
CL ASSIFIFfi BY JLJ rucrifrn BY NEC
GAMMA RAY
ELE
VA
TIO
N (F
T)
821.:
R 1 f , . 3
SI 1 .3
806.3
801.
DATE
RANRF 10 TIMF CONSTaNT 10
10 20
COUNTS/MINUTE
SO 40 90 CO TO BO to
: /~f1
-
"
-
-
-
-
n'm/i?
':
/ ;\
\
\
\\
( :\x
/
CALIPER
HOLE DIAME TER(INCHES)
2 4 6
-
-
:-
-
-
-
-
-
;
:
-
-
nATFlO/H/87
PERMEABILITY
u
E
T
OX
b
t-UJt-
DAT^j/9 i^/f*/
BORING^ORIMG/WELL NO "IW~ II
NOTES
-
87
A "7^ J IUSUNDA IOUCKjjp ~J INOINKM, P.C.
SOIL DATA
u.
I
Q.
10
75
-
•85SITC
AM
PLE
S
bzUl_JQ.
(/>
—
I-:
>-(C
>
UJOL
UJ3
3
—
RFACE ELEVATION
ROCK D A T A
dz
z0
—
2OaLL
Ot-
--
_.._
~
>-
LJ
OuLJtr
0^
886.3
p OF racLtwr, pi FVATION 888.76
QOcr
—
_..
—
—
PA
TE
(W
IN /
FT
)
—
— •
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
f
6S.5'-77.S' LIMESTONE, light olive gray (SY6/1) hard, with faddish mud M 70.0'
77.5-90.0' LIMESTONE, brownish grov (5YR4/1) so f t at 82. 5' and 87.5' grading grayera! 65. 0' with t race block (N1) limoy shale
ROCK
FE
ATU
RE
S
" ,
GE
OLO
GC
OLU
W
\ \
\
"v\\
^S\
II
I
I
^]
1 .
I
L-T
^-p1
T'J"1
r —V-|
11
1
' 1
1
ii
1
WE
LL
CO
LUM
N
n»TF 10/16/87
10/16/87
PHOJFfT TITI F Supplemental Hydrogeolgtc Investigation
Pnn.lFCT NIIMRFR 112.36
1 nrATirvj Lemon Lane Landfill
r.i ASSIFIFD nr JLJ cHFt-KFn RY NEC
GAMMA RAY
EL
EV
AT
ION
(F
T)
821.:
R i r, . :<
8 1 1 . 3
S06.3
SOL:
DATE
RANGE 10 TIMF rON^TAWT TO
10 20
COUNTS/MINUTE
SO 40 30 CO 7O BO »0
___- — ""
(
/• :1
V/
\
\
\\I
X
./
\
-. -~
-
-
-
f
V ' :, , . . / . . :
1 1 X23 /87
CALIPER
HOLE DAMETER
(INCHES!
1 « s
1
-
-
-
-
-
-
-
-
-
-
-
-
\" , ,
DATFlO/U/87
PERMEABILITY
<
i-
u
<n
E
•»
O
X
tfi
K)
i1-</>
t-
*
nAT^/9,9/"/
BORINGA:ORING/WFI 1 NO "
NOTES
-
-
87
zs~y__13? I HAtLAND A IOUCK
~j£~J WOINIIRS, >.C.
SOIL DATA
u.
I
Q.
O
85
91'
SU
rc
SA
MP
LE
S
SA
MP
LE
N
O.
—
RE
CO
VE
RY IF
T)
-
UJ3
<
2.
—
.....
—
ROCK DATA
oz
z^a:
_..
Io(Cu.
—
—
O
—
—
—
ft
o
- -
—
Q0(C
0"
—
—
— -
- —
—
[RA
TE
IMIN
/FT
)
--
• - -
- -
—
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION
SOIL /ROCK CLASSIFICATION
90.0' END OF CORING
RO
CK
F
EA
TU
RE
S
rGE
OL
OG
IC
CO
LU
MN
11
1
1
|
ocirr F| ri/« inw 886.3 nATF 10/16/87
P nr rA<;iur, n FVATION 888.76 10/16/87
WE
LL
CO
LU
MN
pRn.iFrT TITI F Supplemental Hydrogeoloqlc Investigation
PR
LO
n.lFTT NIIMRFR 112.36
rATinw Lemon Lane Landfill
n A<;<;pFipn BY -H-J CHFr-KED HY NEC
GAMMA RAY
EL
EV
AT
ION
(F
T)
796.3
HAwr.F 10 TlUr fONRTANT 10
COUNTS/MINUTE
10 ?o *o 40 so co ro ao 90
II 1 / 1 1 !
(
\
-
.
D4TF 11/23/87
CALIPER
HOLE OIAMETEB
(INCHES)
2 4 C
1 1 1
-
-
-
:-
-
-
-
-
-
n4TF 10/111/87
PERMEABILITY
IUJ
*
(VJ
it-(/)UJh-
*
10
bzi~01UJ1-*
DflT^/fJ.9/W
pnpiNOA'-ORiwn/WFi | wn
NOTES
et
ZJ$' I IUAIIAND * IOUCK
~~7P~T IHQINHW, P.C.
SOIL DATA
.1:i-n.UJo
0
•>
SITC
SA
MP
LE
S
SA
MP
LE
N
O
1
2
3
<*
b
6
SE
CO
VE
HY (F
T)
0;2
.0
1 . ri
1.75
—
_L !
1.0
_j
z
9
9
U
6
—
it
>100
ROCK DATA
Oz
2D<r
1,
2
3
2O<ru.
11 .0
in n
17
ot-
—
-
-
14.
17.
18.
%
RE
CO
VE
RY
-
9J*
42\
QOor
5?
—
—
I'-ll.
X.z3^
tt
—
—
—
—
—
SUBSURFACE LOG
SOIL/ROCK DESCRIPTION|
SOIL /ROCK CLASSIC/CATION
0-4. 01 CLAY, reddish yellow (7/8) t racegravel fragments grading to olive brown(4/4) at 3.8'
< 0 ' -<.2 ' CLAY, silly light rodd.sh brnwn (6M)4.2'-9.B' CLAY, dark red (3.5) wilh rock
black mottled 8.6'-6 8'
9.e'-11.0' CLAY, yellow brown (5/6) brokenlimestone f ragments at 10.6'Boring terminated at 110 '
11.0'-14.4' DOLOSTONE. light gray (N7),
light gray (N8) at 14.0' with glauconitestr ingers; CLAY, greenish gray (5G 6/1) at BRZN
ORZN
14 4'-16 8' NO RECOVERY
mlcrocryttalllne, medium hard, massive17.0S--18.81 DOLOSTONE. lio.hr. Qrav IN7).
RO
CK
FE
AT
UR
ES
sly
GE
OL
OG
ICC
OL
UM
N
'// .
//'
\^-
•>>\.', X X
^ ^ ^
IW
EL
LC
OL
UM
N
or., p ri ruATinN ""-•" n/lTF •-•
n nr r-ASlN,; Fl FVATiON 86°-95 '""" 861. 17 outer 10/16/87
PROJFTT TITLE Supplemental Hydrogeologlc Investigation
PRn.lFPT UIIURFR 112.36
I nrATinw Lemon Lane Landfilln A«inFn m JU/CSS rHFf-KFn HY NtC
GAMMA RAY
ELE
VA
TIO
N
(FT
]
860.6
855.6
850.6
v 8*5.6
RANP.F 10 TIMF rnWSTANT
COUNTS/MINUTE
IO 70 >0 4O 30 SO TO
-
-
-
10
no «o
-
-
-
-
\ -
/\\
\
S
,x
(: (\\\
— L_I — i — i i i / iOATF 1Z/3/87
-
i i
CALIPER
IDLE DIAMETER
(INCHES)
Z 4 C
-
-
-
-
-
~
-
1 1
-
-
-
_
DAIF' 1/19/87
PERMEABILITY
6z
f>UJ
**
(M
0z
VI
*
PO
Oz
IflUJ
nATf-J/'/B'
RORING/tORING/WELL NO """ '2
NOTES
8/23/87 Us«d Gardner Denver 15-Wdrill rig. air ro tary drillthrough soil to 11.0' with4-1/2* tricone roller b i t .CORED from 11. 01 to 20.5'with 3* cor* barrel. Reamedout to 19.5' with 12* triconecollar bit. Set B* I.D steelcasing to 19.5' cemented Inplace.
8/24/87 CORED 'from 20 5' to 58.5'with 3* cora barrel.
6/25/87 CORED Ifom 58.5' to 78 5'with 3' core barrel. Reamedout to 78.5' with B" t f i conerol ler bit. Installed 6-5 /8 1
1 0. steel casing, cemented
8 /31 /07 CORED Irom 78 Y to 98 51
with 3' core bnrrel Rftflmedout core hole to 5 5 / 6 ' witht r i cone roller bir (hole 6-1/8'}. Developed well by air
9/1/87 Packer tes ted C-19/8/3 7 Split spoon sampled wi th
Gardner Denver 15-W dril lrig using 2' I D. spoon
1 1/19/87Caliper logged with Keckcaliper logger .
12/3/87 Gamma ray logged with Keckgama ray loggni
-
:
z 1% f •LASUND i IOUCK"Tp-y BWIMKBS, P.C.
SOIL OATA
u.
r
a
"
20
.30
"40
SU
TC
I
—
d
a.I
t/j
—
a:
UJ(E
—
—
—
— •
S
—
—
—
—
—
—
—
RFACE ELEVATION
P OF CASINO ELEW
ROCK D A T A
Oz
z
4
5
6
—
—
7
Otru.
8.5
20
0.5
—
14.5
-
20
20.;34.5
-
-
44 .
—
—
rrUJ
a
8?
0
170*
—
—
-
on
—
--
860.6
now 860.95 inner
a0a:
—
- -
-
—
RA
TE
(M
IM /F
T)
—
—
--
-
SUBSURFACE LOG
SOIL /ROCK DESCRIPTION
SOIL/ROCK CLASSIFICATION
soft, miciilic at 17.4 ; brown red clay fi l ledvug; calcite fil led vug at 17.5', t race ironand glaconite staining, siliceous breccia at r
1B.6'-19.6' NO RECOVERY19.6'-23.0' DOLOSTONE. light om/e gray5Y 5/2) micrltic. stratif ied, grading to light
olive gray (5Y 6/1). at 21.7' more porousat 22.2' with sparry calcite
f 's
23 0'-25 7' DOLOSTONE. yellowish groy (5Y7/2), micro-crystalline with pale olive (10Y6.2) laminations, glauconite filled f r a c t u r e s2 3 7 ' - 2 3 S ' ; grading palo brown. (SYH 5/?)f l t 25.1' . porous
25 7 ' -2B 4' L IMESTONE, light olivn g ray . '(5Y 6/1) dense, daik g ray (N7) Inminno at26.9' spa r r y c a l c i t p lined lo<;si] f r a g m e n t s f(coral?) at 2Q 4' '
[28:4";29.5' DOLOSTONL". " l i g h t o l ive "qrny " ~\(5Y 6/1) micr i t ic laminated, light g iny (N7)at 29.0' glauconila soecHs at 29.3 . .
/29.5'-30.0' 'SHALE, light g ray (N7) v e r y Tsof t , becoming dolomit ic at 29 65'
,30'-30.r CLAY, medium light grny (NG) ji30.1'-30.5' SHALE, medium_ light gray (N6) |30.5'-3<.5' NO RECOVERY
34.5'-«1.5' LIMESTONE, pale yellowishbrown (10YR 6/2) calclte filled Iraclure(vortical) 34 B'-36 2J. small vugs at 36.25'-36.6' and 36.0', honeycombed weathering at37.25'-37.3'. small brachlopods at 37.3'.grading to light olive gray (5Y 6/1} at38.7'. grading to medium gray (N5) at 39 4'grading (o pal* brown (SYR 5/2) at 41 55'
RO
CK
F
EA
TU
RE
S
— -G
EO
LO
GIC
CO
LU
MN
WE
LL
\
\
"'•
~^"
\
^_
\
Ct
J
\
-]--1-
71 ^
1
1
n/iiP 10/16/87
861 .17 outer 10/16/87
PRn.JFPT T1TI F Supplemental Hydrogeologlc Investlgatiun
PROJECT NUMBER 1'2' 36
1 nrATirvj Lemon Lane Landfil l
CLASSIFIED BY JU/CSS rHFTKFn By "EC
GAMMA RAY
CO
LU
MN
EL
EV
AT
ION
(FT
)
| 840. f
filS.f,
850.6
825.6
820.6
DATE
RANRF '0 TIME
COUNTS
tO ^O 50 40 3
-
-
-
1 112/3/87
/\
\
\
/
/
CON
/MlN
0 I
\X
<;TANT '0
UTE
o 70 to to
\/
-
-
1 1 1
CALIPER
HOLE DIAME TER
(INCHES)
2 4 «
-
-
-
-
.
-
-
OAT
-
-
~
-
-
-
-
f 11/19/87
PERMEABILITY
o2
UJ
DATE
ozt-tnUJD-
•*
O
»-CT)UJ
9/1/87
MW-12
NOTES
-
-
* leits performed at 10 pit .
z —jlffi r SIASUND 1 10UCK~~7P~T INOINKRS, P.C.
SOIL DATA
r
a
n
20
10
-
SiTr
SA
MP
LE
S
SA
MP
LE
N
O
E—
-
—
—
—
RE
CO
VE
RY (
FT
)
-
—
RFACE ELEVA1
P OF CASING E
ut
—
—
:_—
—
ROCK DATA
0z
2tr
4
56
7
I0(ru.
8.5
20
0.5
--
14.5
ot-
20
20.534.1,
--
-
—
—
a
o
a
0
170
69%
—
81*
—
,„„ 860.6
LEGATION 860.95 inner
oorr
- —
—
z2Ui
a:
——
—
—
SUBSURFACE LOG
SOIL /ROCK DESCRIPTION
SOlL/nOCK CLASSIFICATION
soft, micrit ic at 1 7.4 ' ; brown red clay Filled
vug; calcite filled vug at 17.5'. t race iron
18.6--19.61 NO RECOVERY
19.6'-23.0' DOLOSTONE, light ofcve gray
5Y 5/2) micritic. strati f ied, grading to light
olive gray (5Y 6/1). at 21.7' more porous
at 22.2' with sparry calcite
f 's
23.0'-25.7' DOLOSTONE, yellowish groy (5Y
7/2), microcrystalime with pale olive (10Y
6.2) laminations, glauconite Mind t r a c t u i e s
23.7 ' -23.8 ' ; grading pale brown. ( 5YR 5/?)
at 25.1', porous
2S.7 ' -28 .4 ' L I M E S T O N E , light olivo q rny . '
(5Y 6/1) dense, dark g ray |N7) laminnn M
26.9' spa r r y ca lc i to lillod lor.sil t rnqmpnts (
(coral?) at 26 4' f
/?B 4'-59 5' DOLO5TORE7~rTgTii~ olive g r ^ y 1
(5Y 6/1) micri t ic laminated, l ight grny ( N 7 )
'29.5'-30.0' SHALE, light g ray (N7) very 1
soli, becoming dolomitic at 29 65' .\30'-30.V CLAY^ medium light gray (N6) j
30.5 ' -34 5' NO RECOVERY
34.5'-41.5' LIMESTONE, pale yellowish
brown (10YR 6/2) calcite lined Iraclute
(vertical) 34.8'-36.2', small vugs at 36.25'-
36.6' and 36.0', honeycombed weathering at
37.25'-37.3'. smal! brachlopods at 37.3'.
grading to light olive gray (5Y 6/1) at
38.7', grading to medium gray (N5) at 39.4'
P.RZN
TO
CK
FE
AT
UR
ES
f
GE
OL
OG
IC
CO
LU
MN
WE
LL
v.;
J
n
-
~ ;
-•
X
\
•v~ K
-
ii
1 1nATF 10/16/87
861.17 outer 10/16/87
PROJECT TITLE Supplemental Hydrogeo logic Investigation
PROJECT NUMBER "2.36
LOCATION Lemc
CLASSIFIED BY
n Lane Landfill
JLJ/CSS rHFrKFD HY NEC
GAMMA RAY
CO
LU
MN
EL
EV
AT
ION
(F
T)
840.6
-
811). f,
810. f.
825.6
820.6
DATE
riANRF 10 TIMF CONSTANT 10
COUNTS/MINUTE
tO ?0 SO «0 5O to 7O 80 *0
-
-
~
_
-
12/3/87
i / 1 1
/
\
1
\.
/'
\ ;
CALIPER
HOLE DIAME I[R
(INCHES)
1 I
-
-
-
'
-
-
-
-
-
-
OATr'^^/a?
PERMEABILITY
0
t-
OATE
i
UJI-
fO
O
I-
9/1/87
BOPiwr-A-nprur/wFi i MW~I2
NOTES
* lesti performed at 10 pit.
z ~~1/r~~7 ILAILAND i BOUCK~7[ ~) INOINIIRS. P.C.
SOIL DATA
-
SL
0.
SA
MP
LE
N
O
--
.._
—
1—
crUJ
OLJ
ir
—
—
—
UJ
Z
—
"
—
RFiCE E L E V A T I O N
F Or CIS NT. El EV/
BOCK r.'.TA
oz
tt
—
—
•8
—
9
66
3Oau.
—
—
—
-..5
—
—
—
0
-
56.'
—
—
—
—
—
72 .
i?
—
82<>
95S
£
-
-
--
L'
—
—
—
-
—
SUBSURFACE LOG
F.C'i;. /DOCK [ 'E^.CRiPTION
— —
Cfb7^ 1 i/ C L A Y , yelkiv. i:,fi C j i f t y . (5Y 7/7' )
4 i S ' 0 - 4 4 . 3 1 L IMESTONF. pele b r o w n (T.YF15/2) w i t h s p a r r y ca l c i t e specks .
4 4 . 3 ' - 4 5 . 5 ' DOLOSTONE!, O a r k yellow brov.r,. .10YR 4/2) porous
45.6 ' -E0.5 ' LIMESTONE, light olive g ray (iY6/1). s l ight ly laminated, dense, dark q r e y
(N3) 46 .22 ' -46 .36 ' . grading to palp brown( S Y R 5/2) at 47 1 ' . t f> .< i g r a y (N3) 46 1 ' - t
4£ 151. pale b r o w n ( E - V F . f,/2) wiMi purky(wcrr-,y) w e t t h o r i n p e l 4 B . 3 5 1 . s l i g h t l y
laminated, m o d e f f i t e l y p c ( c u s
RF- :? : .
50 5' -52 . 3' S lLTSTOHE . hgni olivp grp.y (^Y ERZr,
6/1). dolomitic
(5_1JB1-52.0' C L A Y , dusky ye l low (5Y 6/4) -
.
(N4) laminated, dark gray (N3) SB am at52 65'. grading dolomiUc at 53 6'. mediumgray (N4), calc i te lined vugs 54 0 ' - 54 ?'
55 .3 ' -58 .5 i NO R E C O V E R Y
58.5'-59.8' SHALE. medium daiK gray. (laminated with darker organic material <
'/i59 B'-BT E' LTDLOSTOTir UgKl g~iay (NIC)mottled with pinkish gray (SYR B/1) pores
linad with calcite, grade* (o light gray (N6) f
laminated SHALE at 61.0'. b recc ia ted at
61.6'-64.65' ' LIMESTONE, light gray (N6)wi th pea-s ized cheM nodu'es
UJ
iu.V
C>0.
- - . .
1-' ^
L\ " *
- -:
^=f= 1
\'
i
:
1 I
1
-' 1
-.-.'—
-L^
i
—•-- ~= .••..; "\
,
Lu.f, [ ) A T f 1U/ I W d -
1 ION St,0-'5'-' nncr S61.1' ' outer 10/16/87
PR
TT;
LL
CL
"i.lFf T NUN'HF R 1 1 ? - ^ f i
V.Tin'J L( '" i ;-' ' '"ne LantJ f i l l
A G S i r i F D fJY JLJ/CSS THFrkFn RY NTG
G A M M A R£Y
% 0_J 1-
815.1
;B I O . C
1
flor, . f
800.fi
HANGf .J^1 1IML CONSTANT LP .
COUNTS/MJNUU
\\
I ::
^^-~^^i ./
\j
\\
x) :/
(: /ii
1 :\
^x^^^\^^
^f/
'VNX
U A l F _ V / V _ f i ^ . . .
Cf tL IPER
10LF niAMEIC"
UNCMCS)
? ^ £
-
-
-
-
-
-
-
-
--
-
-
-
r)ATFn/1^87
EF'M^ ARiLITr
o
DAT E
o
VIUJ
"/I/
o
ft?
Mw~12
N O T E S
-
-
- Icsto per f orilec el 10 |i'.: .
z<3^~ffir~~7 IUJUHD It BOUCK/[ ~} INOINEIRS, P.C
SOIL DAIA
ia
. k<>
70
. 75
. 80
L;
0-'. 3
~. d
r,vs
1
--
—
RE
CO
VE
RY
(FT
)
-
- -
—
——
UJu
5z
z
--
—
SURFACE ELEVATION
ROCK D A T A
0
7Dcr
=
—
10
— '
11
—
—
50au.
—
—
;? .5
78.5
0
—
—
7B. r
_.
92.
—
—
a
^
:j
on
ott
--
• i
SUBSURFACE LOG
ro:L/r,vCK u E S C n i F ' T i o r j
50'L / R O C K C L A S T i r IC/.; l;,fj
6< .85 ' -67 .9 ' LIMESTONE, brownish b leck(SYR 2/1) medium hard, fossiii leious. calc i lc vf
nclusions at 67.1 5 ' -67.35 ' , s l i i nae ts el67 .5 - -67 .9 1
(
sly's67.9'-71.6' LIMESTONE, olive grey (5Y 4/1) . .wilh 0 'aylsH black (N2) ca lcareous SHALE,at 68 8'-6B.9'. waatheied. porous '
!
71 6 ' - 7 4 75 ' L I M E S T O N E . b r o w n i s h gin,-(5rH 4 /1) mic r i t i c po rous . Ihin sea.-i 77' 0'-7 2 0 5 ' g ray ish black (N2j S H A L E . h a r dloss i l i le rous 73 .0 ' -73 .T . and I r e c e l oss i l L to74 75 '
(7 4 . 7 5 ' - 7 5 2 ' L IMESTONE, d a r k g r a y (N?.)micnlic, t r a c e brachiopod f ragmen ls i f
75 .2 ' -76 .5- LIMESTONE, light g ray (N7) wilh f,
76,5:^6^6: CELESTITE ^ •76 .6 - -77 .8 1 SHALE, brownish black (5YR f
2/1}, cBlcaieous, laminatBd '/77 .8 1 - /8 .5 ' - . LIMESTONE, light gray (N7) \ 'micntic maanesium dendr l tes, t f f l ce gi*urnni[ft «;(«
78.6 ' -79.6 ' -DOLOSTONE, dark green g ray
til led vugs |
(5Y 6/1) and medium gray (N4) banded,grade* herder at 80. 5' f
f
eS.OS' -Sa.S ' DOLOSTONE. medium dark f
gray (N4) mlcrltlc lew dark gray (N3) bands
ea.s ' -es.o- LIMESTONE, tight gray (N?)micri t ic, grades dark - g r a y at 64.6'
n
X
utr
__.
T S
-
|v "
|
|!
1
I
T"— , -'-
1 -r
-r-Li
i
,'-
LL^\. ,.j.
X.
,\:r
1•-. '. \" ~" X
-J — ["
^ -J-: ci
1
i.iii1
ii
i
i
\
660. f. D A T F 10/16/87
TOP OF riSltjr, Ft FVATIOrJ 860.95 inner 8 C 1 . I 7 outer 10/16/87
PDUJCL1 T I T L E S plilpmeiit.il H% : • <n;ri;l .it; i r lnvpsti i j . i l (in
P R O . J F C T fJIIMRFR 1 1 7 . 3 6
I O C A T I O I J L p n n Lane LJndt • 1 1
Cl A S S I F l F n Pv .11 . I /CSS r x F r K F D R r N[r-
GAN'MA
EL
EV
AT
ION
(F
T)
•?h..f.
/°0.f,
I
765.1
780.
775.
D A T E
RAY
;,-.N<;i U) T IMT CONSTANT 10
C O U N T S /MINUTE
-
1L /
/
[ 1 1 ]
S :
/--
\ ..
\\
_ no iro no no
- _. ,-- ' ' '
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-
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CALIPER
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(INCHES)
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DATF 11/19/87
P C R M C A B ' L l T Y
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SUBSURFACE LOG
SOIL/ROCK DLV-J i lPMON
SOIL /ROCK Cl ASf . i r i f .ATlOf . 1
f l5 O ' - B B 1 ' ' L l M E S T O f ^ F . da rk g r o > ( N 3 ) ,banded, micri l ic
f
s lyB8.r-94.0' LIMESTONE, medium light gray;N6) tine to medium crystall ine, spa r ry withnoney combed weathering BB.T ' -QS.O '
9-5 C' -98 5' UMtSTONE. llghl grey (NO) line »i>
S l y
98 51 END OF CORING
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SUBSURFACE LOG
SOIL /ROCK K^cniPTlC' . 1
SOIL /ROCK C L A 5 5 H I C A H O M
0-5 5' Fill matenal
5 i'.U.O' CLAY, silly, led
U.0'-20.75- LIMESTONE, v.ry light gray(N7). t race ch«rl and brachlopod losst l
2 . 1 5 i r - n n r f i f l? .36 oulcr 10/16/87
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N C T F S
S/11 /E7 Air i c t c r y dnlleo throuch ic !
to 14 0' wilh 12' inconeroller bil using Gardne rDenver 15-W dnll r i g . Ai t
ro ta iy diill«d througr~ ibediocV to IB.! total depthInstalled 8* s tee l casingCemented In place. Level*C" ptotechon
8/12/87 Air rol«ry dri l led to 58 51
wilh 7-7/6 ' t i icone rol ler bit(hole diamelei 7 -7 /B 1 to 8')Developed well, losing weler
11/17/8 Cal iper logged wi th KnckCfl ipn icggpr
12/3/87 Gumrr.p. rwy loctoc, *i:vi Kn:kgarr.me ra ,- Ic .yu P :
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SUBSURFACE LOG
L,,iL/<,^t',CmMKV.
rOIL / R O T h r ; A ^ F l F l f . / . T i v i r j
20.75'-30.0' LIMESTONE, mridium gray (N5)
LIMESTONE, sof ter at 28.5'
30 0'-37.0' L IMESTONE, medium da rk g r n y(N4) line crys ta l l ine , t /aci , bull L I M E S T O N F
(5B 5/1) with t race yel lowish gray (5Y 8/1)LIMESTONE, hard, solter a! 40.0' and 48.25'
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SUBSURFACE LOG
so:; / R O C K pr^ tRiPi iON
SOIL / H O C K CL .'. r, r.inrAT I O T J
50 0 ' -52 .5 ' UMEEtnNr . yel lo»i : ,M g ' E V(5Y 8/1) modero le ly haid
5J.5--56.D1 VOID. No tecovery
56'. 56. 5' NO R E C O V E R Y
58.5' END OF CORING
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SUBSURFACE LOG
5 5'-12 75' """CLAY", silly, " redd ish bro^n ( < / < ) .t r a c e rock f ragments
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e / i e /67 An r o t a r y dr i l led IhrcugM (il l,s c 1 1 . and bedrock to 1 9 0 'wi th 12' Uicone r o t a r y bitusing a Gaidncr Denver15-W drill rig Set 8' s tee lcasing at 19. i'.
8/19/87 Aif ro tary drilled to 98.5'with 7-7/8* Incone roller bit,set 6-5/B' O D steel casing.Casing was t rern ie g rou ted .
8/20/87 Air r o ta r y drilled wi th S-5/581
(hole diemeler 5 - G / S 1 )
wn ler su rg ingf i / " 1 /B7 Pad-.t-r t P < : e d * c [ ;n / l 7 / 6 7 C n h p e r luggpif *n'i K.P.rt
cahper locjgpi1?/3/87 G«rr.T,n rpy k^C'-d wi!M KetV
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SUBSURFACE LOG
?.C1L /HUL'K UL'-UVin iCV)
SOIL /U("VK ' ! /."ifir;.7 iOr.1
20 0 ' -2U 5' L IMES70NL. mc-Cium grr.y (N5,)t r a c e f o s s i l f i sgmen is . yel lowish g re /(5Y 8 /1 ) at 22. 01
2fe 5 ' - ? 9 0' v e r y soil. cav i l y (?). NOR E T U R N29 0' -30 5' h a r d e r . NO R E T U R N
30 5 - -33 0' s o f t BQBin, c r e v i c e s ' NOR E T U R N
3 3 . 0 ' • 4 0 . 0 ' L I M E S T O N C . medium g r r y ( N 5 ) ,If see brown mud and so f t Q'ay c l ay , hi a iderat 38.0'
40 0' L IMESTONE, ye l lowish g ray (5Y 6/1). hardr Hi/H./t
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SUBSURFACE LOG
r.,,:,,T,v ,.,,.,;,, , • , „ „ ,
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«5.0'-50.0' L IMESTONE, daik g r a y (N3)
t O . O ' - C O . O 1 L IMESTONE:, me^um d a r k g r e y
(Nl), r c l e t i v e l y soil. he rde r at ie.O1
I i ac tu red?
60.0'-67.5' NO RECOVERY
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SUBSURFACE LOG
SOil /r.TJ'K nFT.niFMKV;
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6 7 . 5 ' - 7 5 0' L IMFJSTONE. yel lowish giay(5Y &n) 'me cfysta l l inc, modereleJy hflrd.seller a! e 9 . 0 ' - 7 0 C1
7 5 . 0 - - 7 9 . 0 1 L IMESTONE. dBik gray (N3) .nicr.tii:. ha rder at 77 .75 '
60.0' L IMESTONE, dark O ray (N3). wi thoreyi jh black (N2) shale fiagmenu
80.0'-103- NO RECOVERY
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/.r.-'.ir.Fn ro .M : . • . . • • oirr t.- „, ,,Lt
;" ^
> . . 1
"17 1
K
C ( ' i i r ; ] f. , r,- f j [ l I r
- --'--;•,— ; — ! — i— 1 — i — : —
/'\\
x-..^
"X
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c\
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< i
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y1 1 [- ! 1 1 /I 1 1 ,
D A T F l- ' . ' ' ' f t7
OUiPCr,
"ILL D'flk'l. in-
IUJCHFSI
? 4 C
-
-
-
-
1 1 1
_
-
-
-
-
-
DATE n/1 / / 8 /
,C,,,r,n,;;T,
;-^
r>Ai r P/.^ ' 1* '
K C ' l '.
-
-
-
_
BLASUND I BOUCKiNOINEEBS, P.C. SUBSURFACE LOG
f ,u R E C O V E R Y TO 10:'
103'-107.5' LIMESTONE, llghl c,i,y ( fJ7)f ine gra ined
10 C'.' 7D
/ ~ffi J lUlUNDi BOUCK~W —y INOINEIK, P.C
r Ol DAIA
L
i 10
• \ r
-
Si
Tf
0
n
—
—
—
--
—
—
a
O
LI
—
~
—
—
—
3
—
—
::
—
—
nrAC.E E L E V A T I O N
O
—
—
—
—
—
—
C1
a
—
or>.
C-
—
—
-
:
—
—
:;'
—
—
—
^
—
—
—
—
--
—
—
l '1
—
—
—
—
—
--
SUBSURFACE LOG
.OIL/LOCK,™,.',.,:,,
rr IL /rv ,;">. n Ar.".ir H~;.T uu
107 S ' - lOf i 5 ' L IM iS lONt . mftlii.-iii to l ightg r a y [ f . ' C ) . h e r d1 0 B . 5 ' - 1 10.L1 L I M E S T O N E , as cbovo. *ilhSHALE, mfdium grey (NL)
1 10.5'-113' L IMESTONE, as above, withmore SHALE
11 3.0'- 11 6.0' L I W E S l O f J E . lighl p ray ( f J 7 )rnoderelc 'y haid to sc!l
1 1 C ' - 1 2 - ' - f 1 I M F S I C M . Nt' i l n rn , (N 'i !, ,c
124. 1,1 END OF CORING
'
!'-! :
i
i
ir -1
1
. 1i
i1 .
; i
hbl. i iAir ' D / l b / t /
T r r CAS NO F L E V A T l O N _!S^ .37 HVl l / 7
pn
n;
LC
CL
LL
r? ; i
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D A T E
.M i;", LC- . - L ,-"i. i ,nii!f : : i
/-.^IMLI- HV _Jl ' ' ' (-- ' . CHFfKFr . . P^ N^
r./.f/f.1./. r./.r
R.'.NGF ^ T I M ' CON1<r,T.'.'JT 10 _.
rnijr.' , •_ .- M i r .u l i
i;l ?•• T 4^ -.(•- (,;-, 7!' «P 10
: V. :
f-i1.0—.120 ^\i
/'
1
\
MO
-
-
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C A I 1 r F R
".'1 i" UI/.MI. HI'
; * e
-
-
-
-
-
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I
D A T F ' 1 / 1 7 / 8 7
Li'..
- -
ri.v'.-.Fi m
I
f
0
• o
u ..
-
' • ' - 1 / 6 7
r,MFEi ' OF
r j o ;F r .
-
-
-
* Icr.t '.. per f orr.<.-d J !. 10 [•'', ' .
APPENDIX LL-5
APPENDIX LL-5
PACKER TEST FIELD DATA AND DETAILS
Example of Packer Test Calculation
Permeability equation used 1K = _ Q In Lr
where:
o K = permeability in cm/sec.
o Q = constant flow rate of water into test hole in cmVsec;an average Q value was used in all calculations.
o L = length of hole between packers being tested in feet.
o H = head of water in the test hole in feet.
o r = radius of the test hole in feet.
Conversion factors used 1 psi = 2.31 feet = 70.4 cm1 foot = 30.48 cm1 gal/min = 63.1 cm3/sec
Example calculation for well MW-7 at 20 psi
To find H
H = Depth to water table + height of pressure gauge + gauge pressure= 32.02 feet + 2.6 feet + (20 psi) (2.31 feet) = 80.82 feet
Converting to cm; 80.82 feet x 30.48 cm = 2463.39 cm
To find Q average
Individual Q values were determined by taking the difference in meter readings over a 5 minute interval.
Q, = 22396.8 - 22396.3 = 22.26 gal/min5 min.
Converting; (22.26 gal/min)(6.31 cmVsec) = 1404.61 crrvVsec
Q2 = 22505.8 - 22396.3 = 21.9 gal/min5 min
Converting; (21.9 gal/min)(6.31 cm'/sec) = 1381.89 cmVsec
Q3 = 22615 - 22505.8 = 21.84 gal/min5 min
Converting; (21.84 gal/min)(6.31 cmVsec) = 1378.10 cmVsec
W1MB178K7SZ
Example of Packer Test Calculation (Cont'd.)
Q4 = 22724.2 - 22615.0 = 21.84 gal/min5 min
Converting; (21.84 gal/min)(6.31 cm3/sec) = 1378.10 cm3**
Q average = Q.+Q,+Q,+Q, = 1404.61 + 1381.89 + 1378.1 + 1378.10 = 1385.68 cm4
To find L
L = 94.5 feet - 32 feet = 62.5 feetConverting to cm; (62.5 feet)(30.48 cm) = 1905 cm
To find r/
r = radius of test hole = 2 inchesConverting to cm; (2 inches)(2.54 cm) = 5.08 cm
Solving for K
K = Q In _L(2)(3.14)(L)(H) r
= 1385.68 crrvVsec In 1905 cm(2)(3.14)(1905cm)(2463.39 cm) 5.08cm
= (4.7 x 10-*)(5.93) = 2.8 x 10 * cm/sec
Reference
1. 'U.S. Department of Interior. Bureau of Reclamation. Design of Small Dams' Foundation andConstruction Materials and Laboratory Test. Page 193-196.
17ME7SZ
SINGLE PACKER TEST DETAILS
PROJECT MAMF WesUnghouse, Bloomington Sites r.flRlNG / RORING Mw'7
112.36
LOCATION Lemon Lane Landfill
PERSONNEL JLJ/NEC
nflTF 9/23/87
HEIGHT OF CASINGSTICK UP
.
\_, „, DEPTH TO3Z'02 WATER TABLE
\
X
\
PERFORATED PIPE-
\
\
\
THEIGHT OF GAUGE
I2 6 -
-STEEL
\
ntrpTH 25.0'
DEPTH TOPACKER 32-°'
\
\
^
X
BEDROCK
TEST INTERVAL 62-5 '
\
NOTES:
Performed at 10 and 20 psi .
S~f/? BLASLAND It BOUCKENGINEERS. P.C.
SINGLE PACKER TEST DETAILS
PROJECT NAME "esttnghouse, Bloomington Sites CORING / RnpiMfi m~7
PROJECT NUMBER 112.36 PERSONNEL JLJ/NEG
LOCATION Lemon Lane Landfill DATE 9/23/87
HEIGHT OF GAUGE 2-6 '
1HEIGHT OF CASING
STICK UP
O • \ • X o
\\ DEPT
32.02' WATFR
H TOTABLE
\ / \
X ^ \
\ ' \
HOI F OIAUF.TFR *-°"
r»ppTn 9^.5'
/
-
/—
%o
o
o
0
o
o
o
0
oo
~\
-f'
1
DEP-
PAC
TEST
1
/• ' ^° / ' . '
o .' \ SOIL"^ ^? x
./ \
STFFI r.A«;iNR DFPTH 25.0'
•H TO /KFR 80.0'
\
\ / X
BEDROCK -x
\ ^ \
INTFRVA( 1*.5'
NOTES:
Performed at 10, 20, and 30 psl.
•LASLAND li tOOCKENGINEERS, P.C.
DOUBLE PACKER TEST DETAILS
PROJECT HAUF Westinghouse. Bloom^ngton S<tes CORING / BORING Mw'7
PROJECT NUMBER 112.36 PERSONNEL *££.
Lemon Lane LandfUl O A T F 9/2W87
9T
HEIGHT OF GAUGE 2 '6 '
IHEIGHT OF CASING
STl f tK UP
0 - \ - ^ o
\\ DEPT
»2.Q5' WATER
V
H TOTABLE
\ / \
\ ' pAcKCR '
MOI F OIAMFTFR ^-O"
Jf—
%
^//<
O
o
0
oo
oo
\
^_y
~s//,— f
1
DEPTPAC
TEST
1
'• • ^Q ' : • 'o . \ °'L"^ & ^
/ \STEEL CASING DEPTH 25.0'
rH TO /KFR <».*• ^
\
\ / X
f ^
^~ BEDROCK -x
} \INTFRVAI 15.6'
\
NOTES:
Performed at 10, 20, and 30 pst.
UAIIAMO k MWCK
PROJECT
PROJECT
DOUBLE PACKER TEST DETAILS
Westinghouse. B1oominqton Sites CORING / RnRiNR MW~7
112.36 PERSONNEL 1§£
Lemon Lane Landfill DATE 9/2V87
9T
HEIGHT OF GAUGE 2 '6 '
HEIGHT OF CASINGSTICK IIP
v-^'7\
\ OEPT^2-05' WATER
T
H TOTABLE
\ / \
/ \
\
HOLE DIAMFTFR 4.0"
DFPTH 9*. 5'
f—
^
f~/f'/
\—
0
o
oo
oo
o
7\V,Li
—\s/>— I
+
DEP1PAC
TEST
I
o \ •"""") & ^.
/ \
9TFF1 TA^lNf; HFPTH 25.0"
"H TO /KFR 49.4' X
\
\ / \
^ X
BEDROCK -^
) \INTFRVAI 16.6'
\ ^
NOTES:
Performed at 10 and 20 psi .
BIASLAMO 4 *QUCXINOINIin, P.C.
DOUBLE PACKER TEST DETAILS
MAMFWestlnqhouse. Bloomington Sites CORING / BORING __J?HLZ_
PROJECT NUMBER 112.36 PERSONNEL NEC
i nra-rinM Lemon Lane Landfill DATE _ 9/2f/87
THEIGHT OF GAUGE 2-6 '
tHEIGHT OF CASING
STICK UP
O • ^ o
\
\ DEPT_JtLtO_5' WATER
T
H TOTABLE
\ / \/ PAftf F"R ^
PFF7FnRATFn PlPF
\
HOLF DIAMETFR *.0"
1r-
'//
//<
0
o
0
o
o
oo
7)LJ
—\//_y
DEP1PAC
1
TEST
'
O \ J\ • ^2
/ \_ ^TFFl CASING DFPTH 25.0'
rn TO xKFR «.0' ^
\
\ / ^
^"^ X
^- BEDROCK -s
) \
" v \
NOTES
Performed at 10, 20, and 30 psf .
/J/? KASLAND A•MwvMnHH, P
DOUBLE PACKER TEST DETAILS
PROJECT NAME Westinghouse, Bloomfngton Sttes
PROJECT NUMBER 112i?6
LOCATION Lemon Lane Landfill
CORING / RnRiNfi MW-7
PERSONNEL JLJ
DATE _9/25/87
THEIGHT OF GAUGE 2 -6 '
HEIGHT OF CASINGSTICK UP
0 - \ . ^ o
\
\ DEPT^2.6' WATFR
V
H TOTABLE
\ / \
x ^ \
HOLE niAMFTFR ^.0"
OFPTH 9*.S-
-
'//"
^
o
0
0
o
0
oo
7\^y' >
JJ
-^V/-— /
.
DEP1PAC
TEST
1
/• ' <^* ' - .
o . \ so'L~i c? x
/ \o c n '<;TFFI TA^INR PFPTH t->«u
FH TO . , /-KFR 3 >0
\
\ / X
r -^^ X
^ BEDROCK -,
) \INTFBVAI 10.9'
x \
NOTES:
Performed at 10 and 16 pst .
•LASLANO » BOUCXINOINIIK, PC
PACKER TEST LOG
Project Title Westlnghouse, Bloomlngton SttesTest Date 9/23/87
Project No. n2.36 Boring Diameter(2rl_41.
Location Lemon Lane Landfill
Boring No. VOLO.
Personnel JLJ/NEG
.Casing Height i.98 '
Gauge Height 2-6'
Test No.
1
Depth Interval
To(ft) From(ft)
94.5 32.0
[ Depth toWaterTable
32.02
Height °'Qauge(ft)
2.6
GaugePressure
10 psi
20 psi
j
J-
Meter Reading
Start Finish
21865.0
21953.1
22040.9
22130.0
22285.0
22396.3
22505.8
22615.0
21953.1
22040.9
22130.0
22216.9
22396.3
22505.8
22615.0
22724.2
Time
Start Finish
0
5:00
10:00
15:04
0
5:00
10:00
15:00
5:00
10:00
15.04
20:00
5:00
10:00
15:00
20:00
PACKER TEST LOG
Project Title WesUnqhouse BlooiMngton Sttes Test Date 9/23/87
Project No. H2.36 Boring Diameter(2rl_jL°ll_Location Lemon Lane Landfill
Boring No. J±2Personnel
.Casing Height
Gauge Height .
1.98'
2.6'
Test No.
2
Depth Interval
To(ft) From(ft)
94.5 80.00
[ Depth to.
Water
Table
32.02
Height °'Qauge(ft)
2.6
QaugePressure
10 psl
20 psi
30 psl
Meter Reading
Start Finish
22769.0
22777.6
22786.3
22794.6
22803.5
22832.1
22854.8
22878.1
22909.5
22937.5
22965.3
22993.3
22777.6
22786.3
22794.6
22803.5
22832.1
22854.8
22878.1
22900.3
22937.5
22965.3
22993.3
23021.3
Time
IStart Finish I
0
5:01
10:00
15:00
o
5:00
10:00
15:05
0
5:00
10:00
15:00
5:01
10:00
15:00
20:15
5;00
10:00
15:05
20:00
5:00
10:00
15:00
20:00
PACKER TEST LOG
Project Title Hestinghouse Bloomington Sites Jest Date 9/24/87
Project No. "2.36
Location Lemon Lane Landfill
Boring No. Mw'7
_ Boring Dlameter(2r) 4.0"
.Casing Height i.98»
Gauge Height 2-6 '
Personnel NEC
Test Ho.
3
Depth Interval
To(ft) From(ft)
80.0 64.4
[ Depth to.
Water
Table
42.05
Height of
Gauoe(fl)
2.6
GaugePressure
10 psi
20 psf
30 psl
Meter Reading
Start Finish
23027.4
23027.4
23027.4
23027.4
23028.7
23028.7
23028.75
23028.75
23029.5
23029.5
23029.5
23029.5
23027.4
23027.4
23027.4
23027.4
23028.7
23028.75
23028.75
23028.75
23029.5
23029.5
23029.5
23029.5
1Time
Start Finish
0
5:00
10:00
15:00
0
5:00
10:00
15:00
0
5:00
10:00
15:00
5:00
10:00
15:00
20:00
5:00
10:00
15:00
19:48
5:00
10:00
15:00
20:00
PACKER TEST LOGProject Title Westinghouse B1oomtngton Sites yest Date 9/24/87
Project No. 112.36Location Lemon Lane Landfill
Boring No. M*"7
Personnel NEC
_Boring Diameter(2rl_it°!l.Casing Height 1.96'
Gauge Height 2 -6 '
Test No.
4
Depth Interval
To(ft) From(ft)
66.0 49.4
[" Depth to.WaterTable
42.05
Height of
GaugeUD
2.6
GaugePressure
10 psf
20 psi
Meter Reading
Start Finish
23043.0
23128.1
23193.6
23279.1
23445.0
23547.6
23630.0
23722.5
23128.1
23193.6
23279.1
23344.6
23547.6
23630.0
23722.5
23815.0
Time
Start Finish
0
5:00
10:00
15:00
0
5:00
10:00
15:00
5:00
10:00
15:00
20:00
5:00
10:00
15:00
20:00
PACKER TEST LOG
Project Title Westtnqhouse Bloominqton Sites Test Dflte 9/24/87
Project No. 112.36 Boring Diameter(2r) t.Q"
Location Lemon Lane Landfill
Boring No. HW"7
Personnel NEC
.Casing Height __L2§L.
Gauge Height 2-6 '
Test No.
5
Depth Interval
To(ft) From(ft)
50.6 «.o
[ Depth to.
Water
Table
42.05
Height of
Gauge(ft)
2.6
GaugePresaure
10 psl
20 psf
30 psf
Meter Reading
Start . Finish
23832.5
23838.2
23843.5
23849.0
23860.0
23879.0
23891.9
23907.7
23931.0
23952.7
23974.5
23996.0
23838.2
23843.5
23849.0
23854.3
23879.0
23891.9
23907.7
23923.4
23952.7
23974.5
23996.0
24021 7
ITime
1Start Finish |
0
5:00
10:00
15:00
0
6:00
10:00
15:00
0
5:00
10:00
15:00
5:00
10:00
15:00
20:00
6:00
10:00
15:00
20:00
5:00
10:00
15:00
21:00
PACKER TEST LOG
Project Title Westlnghouse BloorMngton Sites Test Date 9/25/87
Project No. H2.36 Boring Diameter(2rL_ii°lLLocation Lemon Lane Landfill
Boring No. J±Z
Personnel JLJ
.Casing Height
Gauge Height.
1.98'
2.6'
Test Ho.
6
Depth Interval
To(ft) From(ft)
40.9 30.0
Depth to.
WaterTable
42.6
Height °'Gauge(fJ)
2.6
GaugePressure
10 psl
16 pst
Meter Reading
Start ' Finish
24110.0
24194.8
24289.4
24364.5
24485.0
24580.9
24676.9
24772.9
24194.8
24289.4
24364.5
24449.4
24580.9
24676.9
24772.9
24869.1
Time
Start Finish
0
5:00
10:35
15:00
0
5:00
10:00
15:00
5:00
10:35
15:00
20:00
5:00
10:00
15:00
20:00
DOUBLE PACKER TEST DETAILS
PROJECT NAME """nghouse. Bloomlngton Sites COR(N(. /
NUMBER112-36
LOCATION Lemon Lane Landfill
C-2 (MW-10)
PERSONNEL JLJ
DATE 9/15/87
HEIGHT OF CASINGSTICK UP
\
\ DEPTH TO69.t' WATER TABLE
\/
\
PERFORATED PIPE
\
HOLE DIAMFTFR » 5/8"
nFPTH 97.0'
\
\
THEIGHT OF GAUGE 2-6 '
i
\
\DEPTH.
DEPTH TOPACKER 79.9'
/
\
\
^- BEDROCK
\
TEST INTERVAL _LJJ_
NOTES
Performed at 10, 20, and 30 psi .
/ ~JM ftlAILANO k BOUCKrc.
DOUBLE PACKER TEST DETAILS
PROJECT NAME Westinqhouse, Bloomington Sites CORING /
PROJECT NUMBER 112.36 PERSONNEL
LOCATION Lemon Lane Landfill
C-2 (MW-10)
O A T F 9/15/89
^fOF GAUGE 2-6'
IHEIGHT OF CASING
STITK IIP
O • ^ o
\\ DEPT
69.fr' WATER
V
H TOTABLE
\ / \
X ^ \
\
DFPTH 97.0'
1r~
%
f~
//<
O
0
o
0
o
0
o
—\
LJ
— \ty/
.
-t
DEP1PAC
1
TEST
/- ' ^ / . '
/ \
FH TO /KFR 74.9' '
\
\ / X
' /
^- BEDROCK -v
) \IMTFRVAI 7.1'
^ \
NOTES
Performed at 10, 20, and 29 pst .
/~Jyf MJkSLANO & iOOCKOlOINilK. P.C.
DOUBLE PACKER TEST DETAILS
PROJECT MAUF Westinghouse, Bloomington Sites rnffimr. / nnffiMfi C-2 (MW-10)
PROJECT NUMBER 1T2.36 PERSONNEL JU
LOCATION j-emon Lane Landf-tll DATE 9/15/87
HEIGHT OF GAUGE 2 '6 '
iHEIGHT OF CASING
STir K UP _ . . . . . .
1 ^^^
O • x - ^ o
\X 69 k- D£PT
o.? * t \A/ATFR
T
H TOTABLE
\ / \
HOLE niaMFTFR ** 5/8"
nFPTH 97.0'
Jr~
y/
//'\
0
O
O
0
o
oo
'-y
-}
—\//—/
• **• • •
OEP1PAC
TEST
i
-/. ' . 0 / '
o- . \ S01L") G x
/ \^TpFL fi^/NR nfPTH "•"
fH TO /KFR 68.9' '
\
\ / x
r .---•
^~ BEDROCK -,
) \
INTFRVAI 7.1'
X
\ \
NOTES:
Performed at 10, 20, and 30 psl .
KASIAMD * •OOCKINOINHK. P.C.
PACKER TEST LOG
Project Title westinohouse Bioominoton sttes Test Date 9/15/87
Project No. 112.36 Boring Dlameterterl » 5/8"
Location Lemon Lane Landfill .Casing Height Ground Level,
Boring No. c-2 (MW-IO) Gauge Height 2 - 6 '
Personnel JLJ
Test No.
1
Depth Interval
To(ft) From(ft)
87.0 79.9
[ Depth to.WaterTable
69.*
Height of
Oauge(ft)
2.6
GaugePressure
10 psl
20 Psf
30 psf
Meter Reading
Start Finish
19179.0
192^6. f
19311.8
19377.it
mss.o
19569.9
1 9655 . 1
19709.9
1979<t.4
1990^.0
20005.8
20109.6
20205.5
19246. 1
19311.8
19377.*
1 9^5.1
19569.9
19655.1
19689.1
19794.^
19880.1
20005.8
20109.6
20205.5
20309.8
Time
Start Finish
0
5:00
10:00
15:00
0
5:00
10:00
18:30
23:30
0
5:00
10:06
15:20
5:00
10:00
15:00
20:00
5:00
10:00
12:00
23:30
2fl-10
5:00
10:06
15:20
20:00
PACKER TEST LOG
Project Title Westlnghouse Bloomington Sites Jest Date 9/15/87
Project No. 112-36 _Boring Dlameterter) » 5/8"
Location Lemon Lane Landfill
Boring No. c'2 W-"»
.Casing Height Ground Level
Personnel JLJ
Gauge Height 2.6'
Test No.
2
Depth Interval
To(ft) From(ft)
82 74.9
[ Depth to
Water
Table
69.4
Height o'GaugeOU
2.6
GaugePressure
10 psf
20 psi
29 psl
Meter Reading
Start Finish
20565.0
20629.0
20690.9
20754.2
20839.0
20919.0
21 003. if
21085.6
21210.0
21305.8
2H01.3
21497.0
20629.0
20690.9
20754.2
20817.6
20919.0
21003.4
21085.6
21167.8
21305.8
21401.3
21497.0
21594.2
Time
Start Finish
0
5:05
10:00
15:00
0
4:52
10:00
15:00
0
5:00
10:00
1: :00
5:05
10:00
15:00
20:00
4J52
10:00
15:00
20:00
5:00
10:00
15:00
20:05
PACKER TEST LOG
Project Title W«st1nghouse Bloomington Sites Jest Data 9/15/87
Project No. 112.36 Boring Diameter(2r) * 5/a"
Location Lemon Lane Landfill
Boring No. c-2 (Hw-io)
.Casing Height Ground Level
Gauge Height 2.6'
Personnel JLJ
Test No.
3
Depth Interval
To(ft) From(ft)
76 68.9
[ Depth to.
Water
Table
69.4
Height °'Gauge(fl)
2.6
GaugePressure
10 psi
20 psf
30 psl
Meter Reading
Start Finish
21641.5
21650.8
21667.1
21672.7
21680.6
21688.1
21695.8
21703.2
21715.0
21724.8
21732.5
21741.0
21650.8
21667.1
21672.7
21678.5
21688.1
21695.8
21703.2
21710.5
21724.8
21732.5
21741.0
21749.3
Time
Start Finish
0
5:00
10:07
15:00
0
5:00
10:00
15:00
0
5:35
10:00
15:00
5:00
10:07
15:00
20:00
5:00
10:00
15:00
20:00
5:35
10:00
15:00
20:00
SINGLE PACKER TEST DETAILS
PROJECT MAMF Westinqhouse. Bloom-nqton Sites CORINCi / RORlNf, MM-11
PROJECT NUMBER 112.36 PERSONNEL JU
LOCATION Lemon Lane Landfill DATE 9/**/87
HEIGHT OF GAUGE 2 '6 '
1HEIGHT OF CASING
<?TirK IIP
O. - \ - ^ o
\
\ DEPT57.4' WATFR
V
H TOTABLE
\ / \
\ \HOLF DIAMFTFR ., 6-)./8"
PFPTH 90.0'
/
t/ —
YSo
0
o
0
o
0
0
oo
o
— \
yy_/
.
^
DEP1PAC
1
i
TEST
i
// • ±a/ . -o \ SOIL~^ & ^
/ \9TFFI rACSINR OFPTH 15.0'
•H TO /KFR 55.0' /
\
\ / ^
^- BEDROCK -v
\ ^ \
INTFRVAI 35.0'
\ \
NOTES:
Performed at 10, 20, and 30 psi.
KASLAND & BOUCKENGINEERS, P.C.
SINGLE PACKER TEST DETAILS
PROJECT MAMF Westinghouse, Bloomfngton Sttes CORING / BORING Jl*lll_
PROJECT NUMBER 112.36 PERSONNEL J
LOCATION Lemon Lane Landfm HATF 9/9/87
THEIGHT OF GAUGE 2.6'
IHEIGHT OF CASING
STir.K UP
0. - \ - X o
\
^ fi3 03' DEPTD o • u j WATPR
T
H TOTABLE
\ / \
X ^ \
\ \ /
HOLE DIAMETER _L2/§1'
an n *nPPTW 7U«u
-
r-
%o
o
0
oo
oo
o
oo
—\
LJ
-t
DEP1PAC
TEST
1
•** " " * S
o . \ SOIL"7 & x
/ \9TFFI r.A<;iNR OFPTH 15.0'
•H TO /KFR 10.3'
\
\ / X
^ BEDROCK -s
\ ^ \
INTFRVAI 79.9'
NOTES:
Performed at 10, 20, and 30 psf .
•LASLANO k BOUCKtNOiNfiAS, P.C.
PACKER TEST LOG
Project Title Westinghouse Bloomlngton SUes Test Date 9A/87
Project No. 112.36 Boring Diameter(2rl 6 1/8"Location Lemon Lane Landfm
MW-11Boring No.
Personnel JLJ
.Casing Height 2.5 •
Gauge Height i
k
Test No.
1
Depth Interval
To(ft) From(ft)
90 55
[ Depth to.
Water
Table
57. it
Height °'Gauge(fl)
2.6
GaugePreaaure
10 psl
20 psf
30 psl
Meter Reading
Start Finish
17663.0
17671.2
17678.9
17686.8
177W.O
17770.5
17799.2
17828.6
17877.0
17913.3
17950.5
17996.8
17671.2
17678.9
17686.8
1769^.6
17770.5
17799.2
17828.6
17859.1
17913.3
17950.5
17996.8
18028.2
Time ^
Start Finish
0
5:00
10:00
15:00
0
5:00
10:00
15:00
0
5:00
10:00
16:00
5:00
10:00
15:00
20:00
5:00
10:00
15:00
20:09
5:00
10:00
16:00
20:00
PACKER TEST LOG
Project Title Westinghouse Bloomington Sf tes Jest Pate 9/9/87
Project No. "2.36Location Lemon Lane Landfill
Boring No. LU
Personnel JLJ
_Boring Diameter(2r) 6.
.Casing Height 2 .5 '
1/8'
Gauge Height 2 .6 '
Test No.
2
Depth Interval
To(ft) From(ft)
90 10.3
' Depth to.
Water
Table
63.03
Height ofQauge(ft)
2.6
GaugePressure
10 psi
20 psf
30 psl
Meter Reading
Start . Finish
18108.5
18131.0
18152.1
18173.3
18214.0
182*2.9
18283. 4
18299.3
18364.0
8389.8
18426.2
18462.1
18131.0
18152.1
18173.3
18194.5
18242.9
18283.4
18299.3
18326.7
18389.8
18426.2
18462.1
18498.6
Time
Start Finish
0
5:00
10:00
15:00
0
5:03
10:29
15:00
0
5:02
10:04
15:00
5:00
10:00
15:00
20:00
5:03
10:29
15:00
20:00
5:02
10:04
15:00
20:00
SINGLE PACKER TEST DETAILS
PROJECT NAMF Westfnghouse. Bloomlngton Sites CORING / BORING iLJMlllL
NUMBER 112.36 PERSONNEL _CSS
Lemon Lane Landfill DATE 9/1/87
THEIGHT OF GAUGE 2.6 '
IHEIGHT OF CASING
STICK UP
1 ^^^
0. - \ - o
\
9^.5' WATER TABLE
V
\ / \
^ \
ppppno ATFn pirr
\ \ /
HOLE DIAMETFR& 1/8"
nFPTH98.5'
_
•%
0
o
o
0
o
o0
0
oo
~\
(j
•+
^*^^
s- . "- . O /
O . \ ' J & .
/ \1 Q c i
DEPTH TO /PACKFR 78.5'
TEST
1
\ ^
\ / X
' /
^ BEDROCK -,
\ 1 \
INTFRVAI 20. 01
/
\
\ \
NOTES:
Performed at 30 and <*0 psi
S~?/? BLASLAND It BOUCKENGINEERS, P.C.
SINGLE PACKER TEST DETAILS
PROJECT MAMF Hestinghouse. B1oominqton Sites rnRiMfi / PORING C-1 (HW-12)
PROJECT NUMBER 112-36 PERSONNEL css
LOCATION Lemon Lane Landfill DATE 9/1/87
THEIGHT OF GAUGE 2.6'
IHEIGHT OF CASING
STICK IIP
O. - x - X o
\
\ DEPT9^.5' WATFR
V
H TOTABLE
\ / \/
OAPWFD _ ^-
^ / \
\ \ /HOLE niAMFTFP 6 1/8"
PFPTH 98.5'
jr~
%
0
o
o
oo
0
0
o
oo
~\
LJ
1-
DEP1PAC
1
TEST
1
I
S" . ' ' f
/ \
STFFI CASING DFPTH 19.5'
"H TO /KFR 86'
\
\ / X
^- BEDROCK -v
\ J \
INTFRX/fll 12.5'
/
\
NOTES:
Performed at 10, 20, 30, and <tO psf
S~7jr •LASLAND * IOUCKENOINEERS, P.C.
PACKER TEST LOGPage 1 of 2
Project Title Westlnghouse BloorMnqton Sites Test Date 9/1/87
Project No. H2.36 Boring Diameter(2r) 6 1/8"
Location Lemon Lane Landfill
Boring No. (C-D Mw-12
Personnel
.Casing Height
Gauge Height .
.6'
CSS
1
Teat No.
1
2
Depth Interval
To(ft) From(ft)
98.5
98.5
86
78.5
[" Depth to.
Water
Table
94.5
94.5
Height of
Qauge(ft)
2.6
2.6
GaugePressure
10 psf
20 psf
30 psf
40 psf
10
20
30 psl
Meter Reading
Start Finish
0017586.4
0017588.9
0017591.3
0017591.3
0017592.2
0017592.2
0017598.7
17608.4
17608.7
0017612.6
0017613.35
0017613.7
0017614.25
0017614.5
0017586.4
0017588.9
0017591.3
0017591.3
0017592.2
0017592.2
0017598.7
17608.7
17608.8
0017613.3!
0017613.7
0017614.25
0017614.5
0017614.5
ITime >-.,
Start Finish
0
0
0
5:00
0
5:00
0
0
5:00
0
5:00
10:00
15:22
20:00
5:00
5:00
5:00
10:00
5:00
10:00
5:00
5:00
10:00
5:00
10:00
15:22
20:00
25:00
PACKER TEST LOGPage 2 of
Project Title Westlnghouse Blootntngton STtesrrest Date 9/1/87
Project NO. 112.36 ' *
Location Lemon Lane Land'MI 1
Boring No. (c'1
Personnel css
HW'12
Boring Diameter(2r) 6 1/8"
Casing Height -6'
Gauge Height _1^
Test No.
2Cont'd.
Depth Interval
To(ft) From(ft)
98.5 78.5
[ Depth toWaterTable
94.5
Height °'Qauoe(ft)
2.6
GaugePressure
30 psl
W psl
Meter Reading
Start Finish
00176H.5
17615.85
17616.4
17616.7
17617.1
17617.6
0017614.6
17616.4
17616.7
17617.1
17617.6
17617.9
Time
Start Finish
25:00
0
5:00
10:00
15:00
20:00
30:00
5:00
10:00
15:00
20:00
25:00
SINGLE PACKER TEST DETAILS
PROJECT MAUF Westinghouse. Bloominqton Sites CORING / BORING J HLli
PROJECT NUMBER 112.36 PERSONNEL ^LJ
LOCATION Lemon Lane Landfill DATE 8/21/87
HEIGHT OF GAUGE 2 '6 '
iHEIGHT OF CASING
STICK UP
O. • x - X o
\\ DEPT
96.88' WATFR
T
H TOTABLE
\ / \
\ \
HOI F OiAMFTFf*5 6/8" _
OFPTH 123.0'
/
jr—
//t
O
O
O
oo
oo
o
0
o
-)
-}
,
DEPn
PAC
TEST
1
%'. ' : V"-1LV^/ \
- ^TEEL CA^iNR HFPTH 19.0"
PH TO /kFR 113.0'
\
\ / X
^~ BEDROCK -x
\ ^ \
INTFRVAI 10.0'
NOTES:
Performed at 10, 20, and 30 psf
•LASLAND It BOUCKENGINEERS. P.C.
SINGLE PACKER TEST DETAILS
PROJECT MAMF Westlnghouse. Bloomfngton Sttes CORING / RORiNf! MW-U
PROJECT NUMBER 112.36 PERSONNEL JLJ
LOCATION Lemon Lane Landfill DATE 8/21/87
THEIGHT OF GAUGE 2-6 '
1HEIGHT OF CASING
STICK UP
O. • \ - X o
\
\ DEPT96.88' WATER
H TOTABLE
\ / \
X ' \
\ \
nni F niiMFTFR 5 6/8"
npp-TH 123.0'
/
. ir~
%
o0
0
o0
0
o
o
o0
-\
L)
^
DEPlPAC
TEST
I
"o ' ; V"-1^ „ '^/ \
•H TO /KFF? 93. V
\
\ / x
^- BEDROCK -x
INTFRVAI 29.6'
\ ^
NOTES:
Performed at 10, 20, and 30 psi.
•LAS LAND » IOUCKENGINEERS. P.C.
PACKER TEST LOG
Project Title Westlnghouse Bloomlngton S1teSJest Data 8/21/87
Project No. "2-36 Boring Diameter(2rLJ_6/§^Location Lemon Lane Landfill
Boring No. MW-U
Personnel Ju
.Casing Height
Gauge Height 2.6
Test No.
1
Depth Interval
To(ft) From(ft)
123 113
f Depth toWaterTable
96.88
Height of
Gauge(fl)
2.6
Gauge 1 Meter ReadingPressure I
| Start Finish
10 psf J 17510.5II
20 psl
30 psi
R
17510.8
17511.5
17511 .5
17513.3
17513.<t
17513.4
175H.5
17514.5
17515.3
17515.4
17510.8
17511.5
17511.5
17511.5
17513.4
17513.4
17513.4
17514.5
17515.3
17515.4
17515.6
Time
Start Finish
0
5:00
10:00
15:00
0
5:00
15:00
0
5:00
10:00
15:00
5:00
10:00
15:00
20:00
5:00
10:00
20:00
5:00
10:00
15:00
20:00
PACKER TEST LOG
Project Title WesUnqhouse BlooiMnqton SHssTest Date 8/21/87
Project No. H2-36 Boring Dlameterter) s 6/8"
Location Lemon Lane Landfill
MW-14Boring No.
Personnel JLJ
.Casing Height .6'
Gauge Height
Test No.
2
Depth Interval
To(ft) From(ft)
123 93.4
Depth to.WaterTable
96.88
Height °<Qauge(fi)
2.6
GaugePressure
10 psf
20 psl
** 30 psi
Meter Reading
Start Finish
17523.9
17525.4
17526.8
17528.0
17532.2
17536.8
17541.0
17544.4
17567.5
17573.5
17579.4
17585.1
17525.4
17526.8
17528.0
17529.2
17536.8
17541.0
17544.4
17547.7
17573.5
17579.4
17585.1
17591.0
Time
Start Finish
0
5:00
10:00
15:00
0
5:00
10:00
15:00
0
5:00
10:00
15:00
5:00
10:00
15:00
20:00
5:00
10:00
15:00
20:00
5:00
10:00
15:00
20:00
** Note: During the 30 pressure interval test the packer dislodged and moved up the hole. It was reset tothe same depth.
SPS*§
APPENDIX LL-6
-(• J ' - . --r-'ft- '• i»"
APPENDIX LL-6
SLUG TEST FIELD DATA
SLUGCQMP.WKE S.J. Rossello. March 19S8
Proj ect:Project No.:Well No.:Test Date:Formation Tes,ted:
LL SHIP112.36LL EPA--B110/26/87ST.LOUIS LMS
Rising (R) or Falling <F) Head Test:F
Datum height (ft)Static Water Level (ft)Depth to bottom of screen(ft from around level)
Baring Diameter (in)Casing Diameter (in)So sen Diameter (in)Screen Length (ft)Depth to BoundaryDelta H at time O (ft)Delta H at Time t (ft)Time t (seconds)Ratio Kh/KvF'orositv of Filter Pact;
2.0148.37 TOC/ / -rr=-OO . w'wJ
3.502. 002. 005.00SO. OO0.970.23421
K (Bouwer-Rice)K (Hvorslev Time Lag)K (Hvorslev Variable Head)
cm/sec2.1E-32.6E-32.6E-3
-lie: BLUGREDU.WKSCr a cited s January. 1983SLUG TEST DATA REDUCTION
Well No EPA-B1 Initial Depth to water (-ft)jInitial Time (seconds):
Clock Time Depth to water
HR MN Sec
0~T
31214171921~?"T;
262830-T "-»
35_,-.,
3941454751535559
1 61 S1 161 1?1 271 -^
1 412 29
FT IN
48.3747. 1547.5047.7247.6247.8247.8747.9047.9347.9748. 0048. 0248. 0648. 1048. 1248. 1348. 1448. 1943.2O48.2148.2348.2448.2448. 2648.2748.2948.3048.3143.3148.3248.33
El apsedTime inSeconds
0. 003. 008. 00
1 2 . 0 014. 001 7 . OO19.0021 . 0023. 0026. 0023. 0030 . 0032. 0035. 0037.0039. 004 1 . OO45. OO47. 0051.0053. OO55. 0059.0066. 0063. 0076. 0079. 0087. 0093 . 00101.00149. 00
48.370. 00
HeadChangein -feet
0. 001 •'"• —J. . .!_ _<
-0. 37-0. 65-0.. 75-0.55-0.5O- 0 . 47-0. 44
-• 0. 40-0,37-0.. 35-0.31-0. 27-0.25— 0 . 24-0.24-0. IS-O. 13-0. 17-O. 14-0. 13-0. 13-0. 12-0 . 1 0-0. C»9- 0 . 0 7-0. 06-0.. 06— 0 . 05-0. 04
HeadChang*i f : era.
0 . 00-37. 22-26. 43-19. 75-22. 79-16.71-.15. 19-14. 28. _ 1 -T "1 V
-12. 15-11. 24- 1 0 . 63
.... 9 . 4 2-8. 20•-7 . 60-7.29-7. 14-5.47_.rr T
-5.01-4.25- 4 . 1 0-3 . 95-3.49-3.04-2.58-2. 13-1.97- 1 . 32
-j rrr.•~ I • '-/.i
— 1 T? '"?
SLUGCDMP.WKS c. B.J. Rossello, March 19G8
Pro i ect:Project No. :Well No.:Test Date:Formation Tested:
LL SHIP112.36LL EPA-B21O/26/B7ST.LOUIS LMS
Rising '.R) or Falling (F) Head Test: F
Datum height (ft)Static Water Level (ft)Depth to bottom o-f screen(it -from ground level)
Boring Diameter (in)Casing Diameter (in)Screen Diameter (in)Screen Length (-ft)Depth to BoundaryDelta H at time 0 (-ft)Delta H at Time t (ft)Time t (seconds)Ratio Kh/KvPorosits' of Filter Pack
1 . 2065. 12 TOC73.37
3 . 502 . OO2. OO5 . OO
105. OO1.310. 30381
0. 3
K (Bouwer—Rice)K (Hvorslev Time Lag)K (Hvorslev VanablR Head)
cm/sec2.3E-33.0E-32.9E-3
File: GLUGREDU.WKSCreated: January. 1988SLUG TEST DATA REDUCTION
Well No EFA-B2 Initial Depth to water (ft):Initial Time (seconds):
C.1 ock Ti me
HP MN Sec
047
12ia2227T T1
3641465157
1 11 31 101 151 2O1 271 40
Depth
FT
65.65.65 .64.64.64.64.64.64.64.64.64.64.64.64.64.64.64.63.63.
to water
IN
12190500625443-T-T,
27
^ 17130907050301OO9997
El apsedTime inSeconds
0 .4.7.12.18.,-•> ,--,
27."TO
36 .41.46.51.57.61.65.7O.75.80.87.
1OO.
00OO00OO000000000000000000OO00OOOO000000
65.o.
12OO
HeadChangein -feet
0.0 .- 0 .— 0 .— o .-0.--0.-0.-0.-0.-0.1 •
-1.-1.
-I
!•
!•
--1.~~ 1 «
-1.
0007O7•-'*!
50586979859095000406030911121416
HeadCnanuei n c iii .
0.ji .*n
-9.-15.-17.-20.-24.
f-%cr~*- J .
-27.-28.-3O.-31.
-T f-i
— ~ '7l
~ o -.!:• •__~T~^
-34.-34.-35.
001313721977
9600823436^-TJi- •_''
4405661172034809
SLUGCOMP.WKS S.J. Rossello, March 1988
Project: LL SHIPProject No. : 112. 36Well No. : LL EPA-BTest Date: 10/25/37Formation Tested: ST. LOUISRising (R) or Falling (F)
Datum height (ft)Static Water Level (ft)Depth to bottom of screen(ft from ground level)
Boring Diameter (in)Casing Diameter (in)Screen Diameter (in)Screen Length (ft)Depth to BoundaryDelta H at time O (ft)Delta H at Time t (ft)Time t (seconds)Ratio Kh/KvPorositv of Filter Pack
K (Bouwer-Ri ce)K (Hvorslev Time Lag)K (Hvorslev Variable Head)
3
LMSHead Test : F
1.7350. 15 TDC59 . 20
3.502. 002 . OO5.8090.000. 630.23420
1O. 3
cm/sec1.2E-41.6E-41.6E-4
File: SLUGREDLi.. WKSC r s a t e d : 3 a f "i u. a r v , 1988SLUG TEST DATA REDUCTION
Well No
Clock T i
I-IR MN
11
1i11*7\
2*— i
^•—v
-1
"-T
-*
-T
-T
-T-_>
4nrwj
67a89101214
EPA-B3 Initial Depth to water (-Ft):Initial T i me ( sec on a' s ) :
me Depth
Sec F-T
0 50."5 48.13 4G.-inrji. J
'"r1 i;-;i
-T rt
3944475.1564
23-',4r7! 1
4856410152O3141471817304355T»~T
1362102919o4
21
48.49.49.49.49.49,.49.49.49.49.49.49.49.49.49.49.,49.49..•i n*-r "7 n
49.49.49.49,49.49.49.49.49.49.49.49.49.49.50 .50.50.50.
to water
IN
15728299041920T' '""!>
2829~ 23437414549525557596264676970727476777980818487889101000506
LI aosedTi me i nSeconds
0 .5.13.•— tcr-L_ !_' .
•- ' '• j II_, _,.
~^Q
44.47 .51 .56 .64.38.94.99.
108.116,.124.1 3 0 „135.140.151.161.167.1 S 1 .188.197.210.— * -i,— i. -Q .
235.263.301.396.441.480.509.559.600,724.861.
0 o0 00 ( j0 00 000oooo000000000 00 00 0GO00oo0000000 0000000oo0 000oo00000000000000oo000 000
50.0.
15oo
HeadChangein feet
O.-i
-1 .— -\
i. •
•- 1 .- • 0 .— o „-0.—0..— ("j .
-0.-0.-0 .— Q .~~0 n
- 0 .-- 0 .— M B
• - o .-o.—0 .- 0 .—0 ,-o.-0.-0.— o.-0.— 0 .--0.-0.-0.-01.- 0 .-0.-0.-0.-0.—0 .—0 .
0043~^™r
1611969594as86S38278747 Q66636Or-,—iJO
56rr- •-*••-}•-'
51434745434.140383735343129272414151O09
HeadChanqt;i n c m ,
c ._ ji -t-
-40.-f rr
'"" _• •— ' .
— "\ ~r,
- 2 .•-~>ff' ~\_' .1
-2.3.•~> /" " *:. o .1
""jL(b n
-25.-24.-~23 .._. r- T
~2 1 .— 210 .- 1 9 .,-13.•-17.™ 1 / -
- - 1 6 .-15.- 1 4 ..... i 4 .
— 1 .-13.-12.-12.-1 1 .-11.- 1 0 .- 1 0 .-9.•-3.-8.-7
-4.-4._~T•J1 •
— 2 .
0 0444124"7 "?
1636.•3. i.
58i 3.• * .•/ 67o
48•~i — r
051.4
-^ J620 1.L '..'
49o Li
1 367O64600!— .TUH
0963~T ~T
4266202".i"-1
43:-_)4
73
BLUGCQMP.WKS 3.J. Rossello. March 19B8
Proiect: LL SHIPF'r o j ec t No . : 112. 36Wei 1 No. : LL MW-1DTest Date: 10/25/B7Format ion Tested: ST. LOU 1 3Risina (R) or Falling (F)
Datum height (ft)Static Water Level (ft)Depth to bottom of screen(ft -from ground level)
Boring Diameter (in)Casing Diameter (in)Screen Diameter (in)Screen Length (-ft)Depth to BoundarvDelta H at time O (-ft)Delta H at Time t (-ft)T L me t ( sec on d s )Ratio Kh/KvPorasitv o-f Filter Pack
K ( Bouwer-Ri ce )K (Hvorslev Time Lag)K (Hvorslev Variable Head)
LM3Head Test:F
1. 188.66 TOC
55.41
6. 002 . 5O2 . 5010. OO75. 0027. 9O6. OO960
10 . 3
cm/ sec8.3E-59.8E-59.BE-5
Well plugged?
File: SLUGREDU.WKSCreated: January. 1988SLUG TEST DATA REDUCTION
Well No MW-1D Initial Depth to water (ft)Initial Time (seconds)
3.66
Cl
HR
ock Ti
MN
11222:3T,
T;
4444555667778aB999
1112131415161718192025303540
Sec
0344V5917421
314555103056213545561031561235315354952246
~T
2449
JL.004"Tt
o
0ooooo0
Depth to water
FT IN
8.661 0 . 3010.8711.4412.2113.2714.0215. 1215.5916.0116.5917.2118. 1418.9O19.3519.6119.9620. 4020 . 9921.6822. 4123.2023. 7124. 1924.5024.8625. 2325.7226.0826. 4226.9829.2529. 1729.9930.8331.4932.0632.6833. 1433.5934. 1135 . 3936. 1936.6936.98
El apsedTi me i nSeconds
0. 0034 . 0047.0059. 0077.00102. 00121. 00151.00165.001 75 . 0019O. 002 1 0 . OO236. 0026 1 . OO275 . OO285. OO296. OO310. 00•33 1 „ OO
356. 00383. OO413.00435. OO455. 00469. 00485. OO502. 00526. 00543. OO564 . 00589.00662. 00720. OO780. 00844.00903. OO96O. 001022.001 O8O . 001 140.0012OO. 0015OO. 001 SOO . OO2 1 00 . 002400. 00
HeadChangein feet
0 . 001.642.212.783.554.615.366.466.937.357.938.559.4810.2410. 6910.951 1 . 3011.741 2 . 3313.0213.7514.5415.0515.5315.841 6 . 2016.571 7 . 0617.4217.7618.3220 . 5920 . 5 121.3322. 1722 . 8323. 4024 . 0224.4824.9325.4526.7327.5328.0328.32
HeadChangein cm.
'0. '0049.8267. 1484.46107.35140.05162.84196.2521O.53223. 29240.91259.75288. OO31 1 .09324.76332 . 66343. 29356. 66374. 59395.55417. 73441 . 73457.22471 .80481.22492. 16503. 40518.28529. 22539 . 55556.56625.52623.09648.01673.52693.587 1 0 . 89729.73743.70757.37773. 17812.06836.3685 1 . 55860 . 36
SLUGCOMF.WK5 B.J. Rossellu. March 1988
Fro i ect:Pro i ect No. :Well No.:Test Date:Formation Tested:
LL SHIP112.36LL MW-211/3/67ST.LOUIS LMS
Rising (R) or Fallinci <F) Head Test: F
Datum height (ft) 2.93Static Water Level (ft) 52.69 TQCDepth to bottom of screen 65.46(ft from ground level)
Boring Diameter (in) 4.00Casing Diameter (in) 4.0OScreen Diameter (in) 4.00Screen Length (ft) 15.70Depth to Boundary 9O.OODelta H at time 0 (ft) 0.72Delta H at Time t (ft) 0.49Time t (seconds) 1080Ratio Kh/Kv 1Porosity of Filter Pack
K (Bouwer-Rice)K (Hvarslev Time Lag)K (Hvorslev Variable Head)
cm/sec3.0E-54.4E-54.4E-5
Collapse in well.
Tilt; 3LUGREDU. UJK3CreaLed: Janu.arv, 198BSLUG TEST DATA REDUCTION
Wei 1 No MW-2 Initial Depth to water (ft)Initial Time (sec on din)
52.69
lock Ti
R MN
56~j
31012151924304050
1 0
me
St
11T
1
1
2*T
T
rrr_J
42i
0
81B60nr--I
50
9
O
0(I)/
4441
Dep th
i — rI" l
52.51.51.51.51.51.52.52.nr <T.
52.52.52.52.52.52.52.52.52.
to water
IN
69399193O "^
98010204070810172529344043
ElapseTime iSec one
0.G.
11.IS.36.
3 1 0 .— «• -rr--_' .- :-) „
445.5 :l 0 .b39.770.^00.
1 1 30 .1467.3.824.,2404.3 0 0 4 .360 1 ,
•dn
000 00 000000 0000 00 00 00 0000 0000000000 0
HeadChancjei n f ee t.
0 . 00-0., SO-0. 73-0. 77-0 n 74
-0. 71-0.69-0. 67-•0. 65-0. 63-0. 61-0.59-0.52-0.44-0 . 40'-O, 35-0. 2?-0. 26
HeChii n
r-\
"*'2— !..i
~ ^_^
*->
• - ^
- 1
-i-i-i-i-i
-i
-i-
acn -..en
0 n
4.'~r
"T
•"•
1.0 „
C' .,—,
B.
S.7 _
5 .,.1' B
il n
_'' j
3..•' m
!
ei
r'T
"7•~i
-i5S"T
-7
9irr
?S
^16
8~'
'!^j
o.;";,
4
•37
i
5
9-^
2„;
7
S
^1_
",
SLUGCGMP.WKS c. G.J. Rossello. March 19SG
l-'ro i set:F'r o i ect No . :Wei 1 No. :Test Date:Formation Tested:
LL SHIP112.36LL MW--4D11/3/87ST.LOUIS LMS
>.R) or Falling (F) Head Test: F
Datum height (ft)Static Water Level (ft)Depth to bottom of screen(ft -From ground level)
During Diameter (in)C,-asi nq Di ame ter (in)Screen Diameter (in)Sc r een Lengt h (ft)Depth to Eioundar-yDelta H at time 0 (ft)Delta H at Time t (ft)Time t (seconds)Ratio Kh/KvF'orositv of Filter Pack
2.74100.13 TDC122 21
6. OO2.502. 50
1O. OO1S5.OO
1.481.311680
10. 3
K (Bouwer-Rice)K (Hvorslev Time Lag)K (Hvorslev Variable Head)
cm/sec3.2E-64.3E--64.3E-6
File.Cr sci ted »SLUG TE:1
Well No
Clock Ti
MR MN
1^
-T
n?_l
/
10i crJ. --J
1928395160
SLUGREJan LI
T DAT.
MW-4D
me
oeC
(';.
10131 6
62
1641"•*" 1
2O
-T
55wJ U
54-rirr
ii! •— '
IDU. WKSH ;•-*/"='i r •,• „ 1 7 u
-i REDUCT
I n i t i iI
Depth
FT
100.93.93.98.98.98.98.93.93.98.98.98.98.98.93.99.
}QIiJM
*1 Death tonitial TiiTit
to water
IN
136862626459626264667175829O9602
Hattfr ( i t. ) ;; (seconds ) ;
El aosedT i. in e i nSeconds
0 . 0 u1 0 , C' 013.0016. 0066., OO
122.00196. 00341 . 00451 . 006 2 0 . '" • 0903. 00
1 195. 0017 30 .OO2394. 003095.. 003623. 00
1O(if
He,-Charin -F
'!_
-i
-1
- 1
-1
,-1
-1
-1
-1
•]
... J
- 1
•[
•(
— !
-i
' . 1 3. OO
dLit
1
eet
1 . 00.45.51.51.49.54.51.51.49. 47.42.38. 31. 23. 17. 11
HeadC-h-iAOC
i I"1 '_!l
(;, u
-44.
-45.•T C."
— ' I' i J .,
-45,.-•46.-45.-45.-45.-44.-43.n ,
—39 .— 3~" .- "T
— 3"^ .
t.v
u
i j o
05-j •—
'..J ;'
Q7•~~, —7
79o /
s:roil 766i 4
:-?230"^ "7
5472
5.J. Rossello. March 1988
LL SHIP112.36LL MW-510/26/87
Formation Tested: ST.LOU 13 LMSRisinq (R) or Falling <F) Head Test:F
F'ro.i ect :Prelect No.Wei 1 No. :Test Date:
Datum heiqnt (-ft)Static Water Level (ft)Deoth to bottom of screen
(-ft from ground level)Baring Diameter (in)Casing Diameter (in)Screen Diameter (in)Screen Length (ft)Depth to Bound oar vDelta H at time O (ft)Delta H at Time t (Ft)Time t (seconds)Ratio Kh/KvPorc'iiitv of Filter Pack
K ( Eiouwer-Ri ce)K (Hvorslev Time Lag)K ( Hvor s 1 e v V=u~ i ab 1 e Head )
2.51100.43 TOC120.66
6. 002.502.501O. OO185.000.620 . 1 3143
10 . 3
cm/' sec4.9E-46.7E--46. 7E-4
Frile: SLUGREDU. WK3Created: Jarmarv, 1988SLUG TEST DATA REDUCTION
Well No
Clock Ti
HR MN
1111J.
11111ji.
j2ii.±_-7rT;
4
55669
MW--5 Initial Depth to water ( f t ) .Initial Time (seconds):
me
Sec
014172*1)24284553594818212934394553575202735391340599a431341'! r~
Depth
FT
100.99.99.99.99.99.100.1 00.100.100.100.100.100.1 00.100.100.100.100.1 00.1 0 0 .100.100.100 .100.1 00 .100.100.1 OO .100.100.1 00 .1 00 .1 OO .
to water
IN
48788183889002061013161921232526±_ /
28293133•TTT
3638394243444546474848
El a.osedTi me i nSeconds
111111i1
0 .14.J. / a
20 .24.28.45.53.59.64.68.78.a i ..39.94.99.05.13.17.25.40.47.55 .59.193.jj
.*_
20.39 .
249.~r
-T
"7
OS.4-3.78.
401 .555.
0000000 00 0000000000 000Oil'000000000000oo00000 00 00 00 000oooo0000000000
100.0 .4000
HeadChangein feet
0 .-0.-0 .— 0 .•- 0 .-0 .-0.- 0 .- 0 .-0.•- 0 .-0.- 0 ,.o.-0.— 0 .-0.- 0 .-o.— o .-0.-0.-0.-0.-0.-0.— o .-0.-0 .-0.—0 ,— 0 .-0.
0070676560'584642T i — i•-•O
353 .12927.—, cr
-"1 -T
T1 •""?'
.— /— ,
2O1917151312100906050503020 10 000
HeadL t "i a n u (ii n c in .
0 >-2:1 .— 2 0 ,-19.--13." 1 "7 a
— 1 •-• .
-•• i 2 .- 1 1 .— i '". .
... 9 „-8..— P-:
-. ~7
— 6 .
--6.-6.- 6 .
cr
-5.-4 .-4.— "^— "— 2 .-1.-1 ."" i .
-1 .- 0 .-0.— o .—0 ,
oo-7
3S"7 cr-
~1 -•*-
'— • ji.
97765463/ 2312O60996B53OS773 '
5610650473r-i— 77 .'
67"T "7
0661301514
SLUBCDMP.WKS J. March 1 98B
Proiect. : LL SHIPProject No. : 112. 36Well No. : LL MW-8STest Date: 1O/25/G7Formation Tested: ST. LOU 1 3Rising (R) or Falling (F)
Datum height (-ft)Static Water Level (-ft)Depth to bottom o-f screen
'-ft -from ground level)Baring Diameter (in)Casing Diameter (in)Screen Diameter (in)Screen Length (-ft)Depth to Bound arvDelta H at time 0 (-ft)Delta H at Time t (-ft)T i me t ( sec on d s )Ratio Kh/KvF'orositv o-f Filter F'ack
K (BoLiwer— Ri ce)K ( Hvor s 1 ev T i me Lag )K (Hvorslev Variable Head)
LMSHead Test : F
3 . 2O34.55 TDC57.23
6 . 002.502.50
1 0 . 0 072. 001.310.66<?6O
10 . 3
cm/ sec3. 4E-54.4E-54.4E-5
Fil^; SLUGREDU.WKSCreated; January, 1988SLUG TEGT DATA REDUCTION
Well No MW-S3 Initial Depth to water ( f t :Initial Time (seconds)
Clock: Ti
HR MN
11111
2
"-T
-T(
r
-T
-T
-
4445A•7
3891214
16182124
me
Sec
o8173 1A 45328172.14P19•• ~T
44497
j
313651c.- r--J -7
10— .-T
47717858581
1485042c — r-J /
Depth
FT
34.77. .77 .-T" ;
77
77-r-?;
77
77
77T-T
77.
7.7 .
77
33.77 .
77 .
3 3 .
7 7
77-r-r•_" •_' •
-T^T
77 .
7 7
77 .77 .77 .33.• j
77
77,777.7, .-T-T
~r /i_. •34.
t o wi a t e f "
IN
55212422"> rr
262728293 07 O
3133
34~T
36373830404 -1
J.
4142444549• ,J -™<
566164718491940006
Elap-Ti meSecor
r-
17_• i44- — r
6268
3110313915316416918720221 12 1 6231*-, -- i— j-cl- •_' V
— ir_- _.-,
263287307361427488538598721854968
1 170
13021497
edi nds
„ 00. 00„ ooOO
, 00. (DO„ (DO. 00. 00. 00. 00. 00. 'DO. 00., oo. 00. 00. «DO. '•_:''•_ '. O '..'
.- .-.,. - '_•. 00. 00. 00. (DO. 'DO. (DO. 00. (DO. 00oo. OO. (DOoo. 00. 00
hleaCharJ..-I f
?;
••'.1-1
1
•(
— 1"1•~ 1_..
. -^
-1-J
.... I-1... A
~- I
.._ 1
-1— • 1
.,,
-1— 1
-1-1_. ]
-1— 0-O
-0-0-0— O— o— O
— 0
dg eeet
. 00
. 34
. 31_T~T
. 30- 79
'T'CJ
.28
.26
. 26•— >er
. 24• ~ v
. 2 .1„ 2(D, 19.. 18. 17.16. 15
-i er• 1 •_)
. 14
. 13
. 11
. 1O, 06O'~*
. 99.. 94,91,.84.71.64. 61
rr cr. vJ-_'
. 49
HeaCharin c
£-40- 7 9
-40-39- • 7 '-*
- 3 3-38-38-3 8~-~ .^i" /
•_. /— 3 /-36•- 3 6- 3 6-35-35— 3 5-34
"*• .••>~'~ -.J' *+
-34--34— ~*,~r-... -T"7'
• •• 7 '
— "": o-30--28- 27-25-21- 1 9- 1 8-16-14
dQ f-'
IH .
. 'DO
. 71
. 30, 4 i, T ' /'
. 19
. 8(:;^ 7
.29
.13•v p.67. 'D6., / o
4..V. 15. 35, 54. 24. 9 1
"7 Q
.63.-,. ..
7 ---.
. 42
. 20
. 99
. 08
. 56
. 65
.52
.57
.44rr— r
. 71
.8"
SLLJGCOhP. WKS c. B.J. Rossello. March 19SB
Protect: LL SHIPProject No.: 112.36Wei 1 No. : LL MW-8DTest Date: 10/25/87Formation Tested: ST.LOUIS
(R) or Fallinq (F)LMS
Head Test : F
Datum height (-ft)Static Water Level (ft)Depth to bottom of screen(•ft from around level)
Barino Diameter (in)Casing Diameter (in)Screen Diameter (in)Screen Length (ft)Depth to EioundaryDelta H at time 0 (ft)Delta H at Time t (ft)Time t (seconds)Ratio Kh/KvPorositv of Filter Pack
3.5661.12 TDC79. 17
6. OO2.502.5010. OO150.OO
1.360. 61720
1
K (Bouwer-Rice)K (Hvorslev Time Lag)K (Hvorslev Variable Head)
cm/sec5.0E-56.9E-56.8E-5
Well plugged?
F.ile: 3LUGREDU.WK3:...i"'.5iVteu ,: Jarnj.a.r'/. 1 V'j93i_L'G TEGT DATA REDUCTION
Wei 1 No MUI-3D Initial Deoth to we -'-; '. -:' t 'Initial Time '. •=, e c o n cl:; .'•
Cloch Ti
MR MN
11111111
jo<-j
22• -,*-»; r
7
--r
;•>
7;
~r
4
4
4
4cr-o
678910141619-\rr.'.J
iTlfc!
Sec
o1 1141325*~?9
34414550541
13±, -L-
27T;-T
40465216JL. jiL
303- 4.•1 ~r
*'V --'
47'56
ij.
41 226r i *'-s47591230415440-T
4i
O
2057541 7
Depth to water
FT IN
61.1259.6759.6959.7059,, 7259.7359.7459.7559. 7659.7759 . 7959.8259 . 3359.8559.8659.3759. S359 . 3959 . 9059.9259.9359. 9459 „ 9559.9659., 9759 . 9359.9960 . 006O . O 160 . 026 0 . 0 36 0 . 0 260. 0460. 0360. 0960. 1060 . 0760. 1360. 1360.2460. 2960. 3360.3660.4360.5360.5760. 64
F- 1 ~\ p =i fj u
T j. me i nSeconds
0. 001 1 . 0014. 00LG.OO25. 0029 . 0034. OO4 1 . 0045.0050. 0054.0061 . 007B. 0032 . 0037. OO'"' 3 . ("i f i
1 00 . OO1 06 . 00;
112. 00136. 00142. OO150. 00154. OO1 A "'. '".I"!J- \_J -—' II •,• --
1-67. OO176. 00131. 001 S 4 . 0 0i '•••::„ oo21-" 6 . 00216. 002 2 7 . 0 02 3 9 . '"> ("i252.00270. 00261 . 002'? 4 „ 00304 . 00360 . 00427. On434. 00542. 00600,, 00360 . 001017.001194. OO1513.00
He idL (" i ='<. r i u £•in -Feet
0 . 0 0-1.45-1 . 43-1.42- 1.41- 1 . 39-1.38- 1 . 37-1. 36-i. 35-1 - 33- 1.31-1 . 29-1.23-1.27-1 .26- 1 „ 25- 1 . 23-1.22-1.20-1.1 9-1. IB-1.1 7-1.16-1.13-1.14- 1 . 1 4- 1 . 1 3- 1 .. 1 2-1.11- i . ' :>9-1.1 0-1 ,08- 1 . 05-1.03-1 . 03- 1 . 05-1 . 00-0. 94--0.8S-0.84-0. 80-0 . 76-0.64-0.59-0.55-0. 43
H e a •-!C i "l -3. i "i '-! &
I I 1 C Ml .
0 .: 00
-44. 05-43.44-43. 14-42. 6G- *-!• j jj •-
-41. 92- -41 . j2-41. 32-41. 0 1-4O. 41-39. 65-•39. 1?-3E. 73-33.47- '!• b' . L -.'.'...-T-T 3'.-
...-r- -r-7
-37 . Oi-— 36 . -t6
-36. 15-35.85- " ' 5 . "i 4-T; T
-34. 9-"-- — *.! ,--.—
-34. 4S-34. 16-33. 87... -7; — '— — -
-33. 11-33. 42-32.31-31.75-31 .29-31. 14-31.. 90-30. 23
--1O c •'— .L.O • .JO
-26 „ 73
-25 . 37-24. 15-23. 09-19.44— 1 "7 '?'">
-16.71-14.58
SLUGCDMF-1. Wh'S S.J. Rossello, March 1988
Project: LL SHIPProject No. : 1 12.36Well No. : LL MW-9Test Date: 1O/25/87Formation Tested: ST. LOU ISRising (R) or Falling (F)
Datum height (ft)Static Water Level (ft)Dt?pth to bottom of screen(ft from ground level)
Bor i n g D i amet er (in)Casino Diameter (in)Screen Diameter (in)Screen Length (ft)Depth to BoundaryDelta H at time 0 (ft)Delta H at Time t (ft)Time t (seconds)Ratio Kh/KvPorositv of Filter Pack
i< (Bouwer-Rice)K (Hvorslev Time Lag)K (Hvorslev Variable Head)
LMSHead TestrF
2.0652.40 TOC103.33
4 . 004 . OO4.0052.99
1 70. OO0.690.1548O
1
cm/sec1 . OE-41 .5E-41 . 5E-4
File: SLUGREDU.WKSCreated: January, 1988SLUG TEST DATA REDUCTION
Well No MW-9 Initial Depth to water (ft):Initial Time (seconds):
Clock Time
HR MN Sec
111111222223333344445567889910121314
05
13172230343831425374653516294355c
14304151314304830521217193220353575335
Depth
FT
52515151515151515151515151515151515151525252525252525252525252525252525252525252
to water
IN
.40
.68
.72
.73
.74
.76
.78
.79
.81
.85
.86
.88
.90
.91
.93
.94
.95
.96
.98
.00
.01
.02
.03
.05
.07
.08
.09
.10
.11
.15
.16
.19
.21
.24
.26
.27
.30
.33
.34
.36
ElapsedTime inSeconds
05
13172230343863748597106113125136149163175186194210221231243254270288330352372437499512560575635727833875
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
520.40.00
HeadChangein feet
0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-o-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0-0
.00
.72
.68
.67
.66
.64
.63
.62
.60
.55
.54
.52
.50
.49
.48
.46
.45
.44
.42
.40
.39
.38
.37
.35
.34
.33
.31
.30
.29
.26
.24
.22
. 19
.16
.14
.13
.10
.08
.06
.04
HeadChangein cm.
0-21-20-20-20-19-18-18-18-16-16-15-15-14-14-13-13-13-12-12-11-11-11-10-10-9-9-9-8-7-7-6-5-4-4-3-3-2-1-1
.00
.87
.66
.35
.05
.44
.99
.68
.08
.71
.41
.80
.19
.89
.43
.97
.67
.37
.76
.15
.85
.54
.24
.63
. 18
.87
.42
.11
.81
.75
.29
.53
.77
.86
.25
.95
.04
.28
.82
.22
APPENDIX LL-7
APPENDIX LL-7
CALIPER LOGGING FIELD DATA
UASLAND t •OUCKENOINflM, rc.
CALIPER LOGGING
WestinghousePRn..FET Bloomington Sites g|TF Lemon Lane Landfill P E R S O N N E L ^LJ/PDD
PROJECT MO 112.36
11/19/87
MW-2
2.93'
EQUIPMENT DESCRIPTION.
Keck HC-84
WELL/BORING NO CALIBRATION START. 4.0
CASING HEIGHT ABOVE GROUND CALIBRATION END 3.9
PAGE. OF.
D E P T H
69.2
69
68
67
66
65
64
63.39
63.25
63.0
62.75
62.5
62.25
62.00
61.75
61.5
61.25
61.00
60.75
60.50
60.25
60.0
59
58
57
56
55
54
HOLEDIAMETER
4.1"
4.1
4.1
4.1
4.1
4.1
4.1
4.6
4.5
4.5
4.9
4.9
4.8
4.5
4.3
4.3
4.3
4.3
4.2
4.2
4.1
4.1
4.1
4.1
4.1
4.1
4.0
4.0
DEPTH
53 '
52
51.75
51.5
51.0
50.11
50.0
49.75
49.50
49.25
49.00
48.75
48.5
48.25
48.00
47.60
47.5
47.25
47.00
46.0
45
44
43
42.75
42.5
42.25
42.00
41.75
HOLEDIAMETER
4.0 "
4.5
4.3
4.1
4.1
4.8
4.8
4.8
4.3
4 .7
4 .2
4.1
4.1
4.1
4.1
4 . 2 '
4.1
4.1
.,.1
4.1
4.1
4.1
5.2
4.8
4.5
4.6
4.5
4.5
DEPTH
41.5 '
41.25
41.00
40.75
40.5
40.25
40.00
39
38
37
36
35
34
33
32
31.05
31.00
30.75
30.00
29
28
27
26
25
24
23
22
21
HOLEDIAMETER
5.0 "
5.0
5.J s
4.8
4.6
4.2
4 .2
4.1
4.1
4.1
4.1
4.1
4.1
4.1
4.1
6.0
6.0
4.1
4.1
3.8
3.9
3.9
3.9
3.9
3.9
3.9
3.9
3.9
D E P T H
20 '
19
18
17
16
15
14
HOLED I A M E T E R
3.9 "
3.9
3.9
3.9
3.9
3.9
3.9
•LASLANO A IOUCKINOINIIK, ».C.
Westinghouse
PROJECT Bloomingtnn Si t-ps
PROJECT NO 112.36
11/17/87
CALIPER LOGGING
«!ITF T.omrm T ano Tari/jfi l j PERSONNEL. J L J / P D D
DATE
EQUIPMENT DESCRIPTION.
Keck HC-84
WELL/BORING NO MW~3
CASING HEIGHT ABOVE GROUND 3.35 '
CALIBRATION START 4.0"
CALIBRATION FND 4.0"
PAGE. OF.
DEPTH
66.2 '
66.0
64. 3
64.0
63.55
63.25
63
62.75
62.5
62.25
62.0
61.75
61.5
61.0
60.0
59.0
58
57
56.75
56.5
56.25
56.00
56.75
55.5
55.25
55
54.75
54.5
HOLEDIAMETER
5.8 "5.4
5.0
5.0
4.25
4.0
4.0
4.0
4.5
4.1
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.25
4.25
4.5
4.75
4.5
4.5
4.5
5.5
5.5
5.0
4.5
DEPTH
54.25 '54
53
52.1
52
51
50
49
48
47
46
45
44.4
44.25
44.0
43.75
43.5
43.25
43.0
42.0
41.0
40.0
39.75
39.5
39.25
39.0
38.75
38.5
HOLEDIAMETER
A S "
4.5
4.5
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.8
4.8
4.8
4.5
4.25
4.0
4.0
4.0
4.0
4.8
4.9
5.0
5.1
5.0
4.5
4.25
DEPTH
1R J^ '
38.0
37
36
35.75
35.5
35.25
35.0
34.0
33.0
32.0
31.0
30.0
29.0
28.0
27
26
25
24
23
27.75
22.5
22.25
22.0
21.0
20.0
19
18
HOLEDIAMETER
/, r> "
4.0
4.0
4.25
4.25
4.25
4.25
4.0
4.0
4.1
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.5
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
DEPTH
17*16
HOLEDIAMETER
l\ 0 "4.0
•LASIANO * KNICKINOINHK. P.C.
CALIPER LOGGING
Westinghouse
PROJECT Bloomington Sites
PROJECT Nn 112.36
11/16/87
MW-4I
<;ITF Lemon Lane Landfill P E R S O N N E L JLJ/PDD
DATE
EQUIPMENT DESCRIPTION
Keck HC-84
WELL/BORING NO.
CASING HEIGHT ABOVE GROUND L '92 '
CALIBRATION START 3.0
CALIBRATION FMO 3.5
PAGE.
DEPTH
93.07 '
93.0
92.0
91.0
90.0
89
88
87
86.3
'86
85
84
83
82
81
80.75
80.5
80.25
80.0
79.75
79.5
79.25
79.0
78
77
76
75
74
HOLEDIAMETER
3.4 "
3.5
3.5
3.5
3.5
3.5
3.5
3.4
3.7
3.5
3.5
3.5
3.4
3.4
4.4
4.0
3.8
3.6
4.0
3.8
3.6
3.6
3.6
3.5
3.6
3.6
3.5
3.5
DEPTH
73 '
72
71
70
69
68.75
68.5
68.25
68
67
66
65
64
63
62
61
60
59
58.31
58.25
58
57.75
57.5
57
56
55
54
53
HOLEDIAMETER
3.6 "
3.5
3.5
3.6
3.8
3.8
3.6
3.9
3.6
3.6
3.6
3.8
3.8
3.6
3.6
3.5"
3.7
3.8
4.2
4.3
4.2
4.1
4.1
3.9
3.7
3.9
3.5
3.5
DEPTH
52'
51
50
49
48
47
46
45
44
43
42
41.65
41.5
41.25
41
40.3
40.25
40
39
38
37
36
35
34
33
32
31
30
HOLEDIAMETER
3.6"
3.8
3.6
3.5
3.6
3.5
3.7
3.8
3.6
3.6
3.8
4.7
4.7
5.1
4.8
4
4
3.8
3.7
3.7
3.7
3.6
3.5
3.6
3.6
3.5
3.5
3.5
DEPTH
29 r
28
27
26
25
24
23
22
21
20
19
18
17'
16
15
14
13
12
11.22
11
10
9
8
7
6
5
HOLEDIAMETER
3.5"
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.5
3.9 *
3.2
3.5
3.5
3.5
3.5
3.5
3.5
3.5
•Uf LAND t IOUCKBMMNIIK, f.C.
Westinghouse
CALIPER LOGGING
PROJECT. p f-on g i t-oc g[TF Lemon Lane Landfil l P Fp«;r)MMFi JLJ/PDD
PROJECT NO.112.36
DATE 11/16/87EQUIPMENT DESCRIPTION.
Keck HC-84
WELL /BORING NOmeasuring point
MW-7 CALIBRATION START. 3"/3'
ABOVE GROUND2.15'
CALIBRATION END_
PAGE L OF_1
4.6"/4.0"
DEPTH
95.55'
95.00
94.0
93
92
91
90
89.05
89.0
88.75
88.50
88.00
87.00
86.00
85.00
84.04
84
83.75
83.5
83.25
83.0
82.75
82.5
82.25
82.0
81.0
80.0
79.0
HOLEDIAMETER
3.75"
3.75
3.75
3.75
3.75
3.75
3.75
4.00
4.00
3.90
3.75
3.75
3.75
3.75
3.75
4.5
4.6
4.2
4.0
3.9
3.9
3.9
3.8
3.75
3.75
3.75
3.7C
3.9
DEPTH
78'
77
76
75
74
73
72
71
70
69
68
67
66
65
64.75
64.5
64.25
64.0
63.75
63.5
63.25
63.00
62.75
62.50
62.25
62
61.75
61.50
HOLEDIAMETER
3.75 "
3.75
3.75
3.75
3.75
3.75
3.75
3.75
3.75
3.75
3.75
3.75
3.75
4.00
3.8
3.8
3.9
3.9
3.8
3.9
4.2
4.2
4.4
4.1
4.1
4.1
4.2
4.2
D E P T H
61.0'
60
59
58.06
58.0
57.04
57.0
56.75
56.5
56.25
56.0
55.75
55.5
55.25
55.0
54.75
54.5
54.25
54.0
53.75
53.5
53.25
53
52.75
52.50
52.25
52.0
51
HOLEDIAMETER
4.0"
3.75
4.0
4.0
4.0
4.4
4.4
4.9
5.0
4.8
4.8
4.8
4.5
4.4
4.5
4.9
4.8
4.4
4.0
3.9
4.0
4.0
3.9
3.8
3.8
3.8
3.8
3.75
D E P T H
50.25'
50
49.75
49.5
49.25
49
48
47
46.75
46.5
46.25
46.0
45.80
• 45.5
45.25
45.00
44.75
44.50
44.25
44.00
43.75
43.5
43.25
43.00
42.75
42.5
42.25
42
HOLED I A M E T E R
4.1"
4.0
4.0
4.2
4.0
3.75
3.75
4.1
4.1
4 . 2
4.2
4 .2
4.8
4.9
4.9
4.8
4.5
4.1
4.2
4.8
5.0
4.9
4.9
a. 84.9
5.4
5.05.1
•UkSLANO ft MUCKINOINIIK. P.O.
CALIPER LOGGING
Westinghouse
PROJECT Bloomington Sites SITF Lemon Lane LandfillPFRSONNFI JLJ/PDD
PROJECT MO 112.36 EQUIPMENT DESCRIPTION.
DATE H/16/87 Keck HC-84
WELL/BORING {Jn MW-7 CALIBRATION START 3"/3"measuring pointXXSItlGcHKtGCtir ABOVE GROUND 2.15 CALIBRATION FMO 4.6"/4.0"
PAGE. OF.
DEPTH
41.83'
41.75
41 50
41.25
41
40.75
40.5
40.25
40.0
39.75
39.5
39.25
39.8
38.75
38.5
38.25
38
37.62
37.5
37.25
37.0
36.75
36.50
36.25
36.0
35.75
35.5
35.25
HOLEDIAMETER
6.5 "
6.8
5.9
4.9
4.2
4.6
4.8
4.9
4.3
4.3
4.5
4.3
4.1
4.0
3.9
3.8
3.8
4.0
4.0
4.1
4.1
3.9
4.5
6.8
8.1
7.5
6.7
6.5
DEPTH
35.0'
34.75
34.5
34.25
34.00
33.75
33.5
33:25
33.00
32.75
32.5
32.25
32.00
31.75
31.5
31.25
31.0
30.75
30.5
30.25
30.00
29.75
29.5
***29.5
28.31
28.00
27.75
27.50
HOLEDIAMETER
6.1"
6.0
5.9
5.4
4.9
4.9
4.8
4.5
4.3
4.3
4.5
4.5
4.5
4.2
4.1
3^9
3.9
4.4
4.0
3.9
3.9
6.8
10.5
7.5
5.1
4.9
4.5
DEPTH
27.25'
27.0
26.75
26.50
26.25
26.0
25.0
24.0
HOLEDIAMETER
4.5"
4.5
4.5 ^
4.5
4.5
4.9
4.6
4.6
DEPTH HOLEDIAMETER
*** stuck - had to yank to get out
•LASLANO » lOUCKIMOINIHS, *.C.
CALIPER LOGGING
Westinghouseppn.lFf.T R1 oomlngton Sites
PROJECT Mr> 112.36
SITF Lemon Lane Landfill P P R S D M N F I JLJ/DAT.
DATE 11/19/87
WELL / BORING NO. MW-9
EQUIPMENT DESCRIPTION.
Keck. HC-84
CASING HEIGHT ABOVE GROUND 2.06'
CALIBRATION START 4.0"/4.Q"
CALIBRATION FNH 3.7"/4.0"
1 1PAGE. OF.
DEPTH
106.8 '106.08
105
104
103
102
101
100
99
98
97
96
95
94
93
92
91
90
89
88
87
86
85
84
83
82
81
80
HOLEDIAMETER
3.9 "
3.9
3.9
3.9
3.9
3.9
3.9
3.9
4.0
4.0
4.0
4.0
4.0
4.1
4 .2
4.0
4.0
4.0
4.0
3.9
3.9
3.9
3.9
3.9
3.9
3.9
3.9
4.0
DEPTH
79 '78
77
75
74
73
72
71
70
69
68
67
66.26
66.00
65.75
65.5
65.25
65
64
63
62
61
60
59
58
57
56
55.27
HOLEDIAMETER
3.9"
3.9
3.9
3.9
4.2
4.0
4.0
4.0
4.0
4.0
4.0
3.9
4.2
4.1
4.8
4.5
4.2
4.2
3.9
4.0
3.9
3.9
3.8
4.1
3.9
3.8
3.8
4.2
D E P T H
55 '54
53.9
53.75
53.5
53.0
52.0
51.0
50.0
49.0
48.0
47.0
46.0
45.20
45.00
44.75
44.50
44.25
44.0
43.75
43.5
43.25
43.00
42.00
41.00
40.00
39.00
38-00
HOLEDIAMETER
4.0"
4.0
4.2
4.2
4.0
3.9
3.9
3.9
3.9
3.9
3.9
3.8
3.9
4.2
4.2
4.8
5.5
5.9
4.9
4.5
4.3
4.3
4.0
4.0
4.0
4.0
4.7
3.9
D E P T H
37.0 '
36.0
35.0
34.0
33.0
32.0
31.0
30.0
29.0
28.0
27.0
26.75
26.5
26.2526.00
25
24
23
22
21
20
19
HOLED I A M E T E R
3.9 "
3.9
3.9
3.9
4.1
3.9
3.8
3.9
4.1
4.0
5.7
5.2
3.8
3.8
3.5
3.5
3.5
3.5
3.7
3.7
3.7
3.7
•LASLANO A IOUCXINOWHK. r.C.
CALIPER LOGGING
PROJECT
PROJECT NO
WestinghouseBloomingt.nn Sites SITE T.anp T.andfi 1 1 PFBSnMNFI .TT..T/rgS
H2.36
10/14/87
WELL /BORING NO MW-11
EQUIPMENT DESCRIPTION.
HC-84
CASING HEIGHT ABOVE GROUND 2.46
CALIBRATION STAPT 6 l/8"/6 1/8"
CALIBRATION FMH 6 l/8"/6 1/8"
PAGE.1
OF.1
D E P T H
90.1 '
89.5
89
88
87
86.65
86.5
86.25
86
85.75
85.5
85.25
85
84
83
82
81
8079.9
79
78.8
78
77
76
75
74
73
72.3
HOLEDIAMETER
6.1 "
6.0
6.1
6.1
6.1
6.5
7.0
6.5
7.1
6.75*
6.5
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.2
6.1
6.5
6.1
6.1
6.2
6.2
6.5
6.1 "blip"
7.0
DEPTH
72 '
71.7
71
70
69.7
69
68
67
66
65
64.8
64.5
64.25
64.0
63.75
63.50
63.25
6 T . r >62.75
62
61
60
59
58
57
56
55
54
HOLEDIAMETER
6.2 "
6.5
6.1
6.2
6.25
6.2
6.1
blip
blip
6.3
6.8
7.1
6.9
6.7
6.5
6.5
6.5
6.1
6.2
6.1
6.1
6.1
6.1
6.1
6.1
blip
6.1
6.1
DEPTH
53 '
52
50
49
48
47.5
47
46
45
44
43
42
41
40
39
38
37
Tfi
35
34
33
32
31
30
29
28
27
26
HOLEDIAMETER
6.4
6.1
6.1
6.1
blip
6.5
6.2
6.2
6.2
6.1
6.1
blip
blip
6.1
6.1
6.1
6.1
6.1
6.1
6.1
blip
6.1
6.1
6.1
6.1
6.1
6.1
6.1
D E P T H
25 '
24
23
22
21
20
19.65
19.5
19.25
19
18
17.2
17.0
16
15
14
HOLEDIAMETER
6.1 "
6.1
6.2
6.1
blip
6.1
6.8
6.7
6.0
6.0
6.1
6.5
6.3
6.2
6.2
6.2
** Note: Blip is a slight needle movement.
•LASLAND * tOOCKHMMNliM, P.O.
CALIPER LOGGING
Westinghouse
PRO.iECT Sites SITF Lemon Lane Landfill
112.36PROJECT NO.
DATE_ll/19/87_
WELL / BORING NO. MW-12measuring point„—. ; ABOVE GROUND 1.05'
EQUIPMENT DESCRIPTION.
Keck HC-84
CALIBRATION START 6 1/6"6 1/6"
CALIBRATION END
PAGE. OF.
DEPTH
100.49*
100
99
98
97
96
95
94
93
92
91
90
89
88
87
86
85
84
83.75
83.5
83.25
83
82.75
82.5
82.25
82
81
80
HOLEDIAMETER
6.2"
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.1
6.0
6.0
5.9
5.9
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
6.0
6.6
6
5.7
5.8
5.7
5.8
DEPTH
79.25*
79
78
79
76
75
74
73
72
71
70
69
68
67
66
65
64
63
62
61
60
59
58
57
56
55
54
53
HOLEDIAMETER
ii6.0
5.9
5.9
6.0
5.9
5.8
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.1
6.0
6.0
6.0
6.0
6.0
6.0
DEPTH
52 '
51
50
49
In casir
HOLEDIAMETER
ii6
6
6
6
g 6
DEPTH HOLEDIAMETER
•LASIAND 4 BOUCXIN4MNUM, PC.
Westinghouse
PROJECT Bloomington Sites
PROJECT Kin 112.36
DATE 11/17/87
WELL /BORING Mn MW-13
CALIPER LOGGING
Lemon Lane Landfill PPPQI-IMMFI JLJ/PDD
EQUIPMENT DESCRIPTION
Keck HC-84
CASING HEIGHT ABOVE flRniiNn at ground level
CALIBRATION START 8.0"
CALIBRATION FKin 8.1—
1 „ 1PAGE. OF.
DEPTH
56.03'
55.75
55.5
55.25
55
54.7
54.5
54.25
54.0
53.75
53.5
53.25
53.0
52
51
50
49
48
47
46
45
44
43
42
41
40
39
38
HOLEDIAMETER
9.5"
17.5
17.5
17.5
14.5
16.0
16.3
14.8
11.8
10.3
9.0
9.0
8.1
8.1
8.1
8.1
7.9
7.9
7.9
7.9
7.9
7.9
7.9
7.9
7.9
8.1
8.1
8.1
DEPTH
37.89 '
37
36
35
34
33
32
31
30
29
28
27
26
25
24
23
22
21
20
19
18
17
16
15
14
HOLEDIAMETER8.8"
8.8
8.0
8.1
8.0
8.0
8.0
8.0
8.0
7.9
7.9
7.9
7.9
7.9
7.9
7.9
7.9
7.9
8.1
8.1
8.1
8.1
8.1
8.1
8.1
DEPTH HOLEDIAMETER
-
DEPTH HOLEDIAMETER
KASLAMD * 1OUCKf.C.
CALIPER LOGGING
WestinghousePROJECT BldOTningt-nn Sites
PROJECT Mf> 112.36
<!ITF Lemon T.anp Landfill PERSONNEL _JLJ/ELIL
11/7/87
WELL /BORING Mn MW-14
EQUIPMENT DESCRIPTION.
Keck Hr-ftA
CASING HEIGHT ABOVE GROUND 2.27
CALIBRATION START 3"/?"
CALIBRATION FNH fi.V'/fi.fl"
PAGE 1 OF .
DEPTH
126.32'
126.0
125.0
124.0
123.0
122
120
119
118
117
116
115
114
113
112
111.25
111
110
109
108.54
108.5
108
107
106
105
104
103
102
HOLEDIAMETER
5.8"
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
5.8
Blip 5.8
5.8
5.8
5.8
6.5
6.5
5.8
5.8
6.2
6.2
6.4
6.4
6.4
DEPTH
ior100
99
98
97
96
95
94
93
92
91
90
89
88
87
86
85
84
83
82
81
80
79
78
77
76
75
74
HOLEDIAMETER
£. 1 "6.4
6.46.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
6.2
DEPTH
73'
7271
70
69
68
67
66
65
64
63
62
61
60
59
58
57
56
55
54
53
52
51
50
49
48
47
46
HOLEDIAMETER
6.2"
6.26.2
6.2
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
DEPTH
451
44
43
42
41
40
39
38
37
36
35
34
33
32
31
30
29
28
27
26
25
24
23
22
21
20
19
18
HOLEDIAMETER
ii6.1
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
6.3
UASIANO » IOUCKWOINHK, f.C.
Westinghouse
PROJECT RlnoTningt-on Si tog
PROJECT Kin 112.36
DATE _yV7/87_
WELL/BORING Kin MW-14
CALIPER LOGGING
SITF T.pmnn T.ana PFRtJONNFI .IT..T/Pnn
EQUIPMENT DESCRIPTION.
Kp.r.k HC.-RL
CALIBRATION START 3"/3"
CASING HEIGHT ABOVE GROUND 2.27 ' CALIBRATION FSin 6.3"/6.0"
2 ._ 2PAGE. OF.
DEPTH
17 '
16
15
14
13
12
HOLEDIAMETER
6.3 "
6.3
6.3
6.3
6.3
6.3
DEPTH HOLEDIAMETER DEPTH HOLE
DIAMETER DEPTH HOLEDIAMETER
APPENDIX LL-8
APPENDIX LL-8
GAMMA RAY LOGGING FIELD DATA
•IA11ANO It IOUCKIMOINHM. P.C.
GAMMA RAY LOGGING
Westinghouse Bloomingt^prp- Lemon Lane Landfill PERSONNEL_£L^Sites
PRD.IFf-T NO 11236
HATF 9/16/87
WFL I /BORING NO C-2 (MW-10)
F| nip | EVFI H. 12 TOG
P, urn WaterReference Pt. c 01 .ilfMSffffGXVKMUfK AROVF fiRQiiNn 5.81
EQUIPMENT DESCRI
Keck GR-81
BACKGROUND STAR
BACKGROUND END
TIME CONSTANT
RANRF 10
IPTIDN
T 36.5
35.5
10
PAGE
T I M E
2: 30pm
3: 18pm
3: 19pm
3: 20pm
3:21
3:22
3:43
3:44
3:45
3:46
3:47
3:48
3:49
3:50
3:51
3:53
3:54
3:55
3:55
3:56
3:57
3:58
3:59
4:00
D E P T H
102.32
101.32
101
100
99
98
97
96
95
94
93.5
93
92.5
92
95
91
90.5
90
89.5
89
88.5
88
87.5
87.0
COUNTS
43
40.5
35.5
33.5
47.5
45.5
50.5
73
82.5
75.5
72.5
62.5
58.5
58
51
80
112
123
111
105
76
54.5
56.0
60.0
TIME
4:01pm
4:02pit4:02.3
4:03
4:04
4:05
4:06
4:06.3
4:07
4:08
4:09
4:09.3
4:10
4:11
4:12
4:13
4:14
4:15
4:16
4:17
4:17. 3'
4:18
4:18.5
4:19
DEPTH
86.5'
86
> 85.5
85
84.5
84
83.5
) 83
82.5
82
81.5
D 81
80.5
80
79.5
79
78.5
78
77.5
77
76.5
76
75.5
75
COUNTS
67.5
75
78.5
82.5
64.5
66
53.5
47.5
49.5
41.5
38.5
36.0
48.0
79.0
60.5
48.0
75.5
110
105
60.5
52.5
37.5
28.5
34.5
T I M E
4: 20pm
4:21pm
4:22
4:23
4:23.5
4:24
4:25
4:26
4:27
4:27. 3(
4:29
4:30
4:31
4:32
4:33
4:34
4:35
4:37
4:38
4:38.30
4:39
4:39.30
4:40
4:42
D E P T H
74.5'
74.0
73.5
73.0
72
71.0
70.0
69
68
67
66
65
64
63
62
61 '
60
59
58
57
56
55
54
53
COUNTS
29.5
27.5
70.0
78.0
39.5
42
40.5
45.5
42.5
30.5
25.5
31.0
58.5
115.5
132.0
119.5
59.5
50 ..5
37.5
30
27.5
38.5
31.0
43
T I M E
4:42.3
4:43
4:44
4:45
4:46
4:46.5
4:47
4:48
4:49
4:51
4:52
4:53
4:54
4:55
4:56
4:56. 3(
4:57
4:58
4:59
5:01
5:02
5:02. 3C
5:03
5:04
D E P T H
ipm52 •
51
50
49
48
47
46
45
44
43
42
41
40
39
38
37
36
35
34
33
32
31
30
29
COUNTS
41.5
84
101
43
33
49.5
99.5
130
80
60
56
67.5
59
64
69
86.5
64.5
69.5
66
55.5
69.5
74.5
61.5
57.5
UASLANO * IOUCKiMOINHM, r.C.
GAMMA RAY LOGGING
Westinghouse BloomingtofrF Lemon Lane Landfill PERSONNEL_JLJSites
PROJECT ND 112.36 EQUIPMENT DESCRIPTION.
9/16/87
WELL /BORING NO. C-2 (MW-10)
FLUID LEVEL 71.12 TOG
FI ,nn water
GROUND _5-JU_
Keck GR-81
BACKGROUND START 36. S
BACKGROUND END__15^5__
TIME CONSTANT.
10
in
RANGE.
PAGE OF.
T I M E
5:06
5:07
5:08
5:09
5:10
5:11
5:13
5:14
5:16
5:17
5:18
5:21
5:22
5:23
5:24
5:24.30
5:25
5:26
5:27
5:28
5:29
5:30
5:31
5:32
D E P T H
28'
27
26
25
24
23
22
21
20
19
18
17
16
15
14
13
12
11
10
9
8
7
6
5
COUNTS
80.5
85.5
88.5
88.5
107.5
90.5
82.5
87.5
69.5
69.5
61.5
48
42.5
48
40.5
77.5
108.2
111
105
108
105
112.5
90
48
T I M E DEPTH COUNTS T I M E D E P T H COUNTS T I M E D E P T H COUNTS
•LASLAND * KXfCXINO1NIIK, P.C.
GAMMA RAY LOGGING
WestinghousePROJECT Bloomington Sites
PROJECT MO 112.36
11/23/87
WELL /BORING NO. MW-11
FLUID LEVEL 66.98 TOG
FLUID water
SITE Lemon Lane Landfill
reference point „ ..." ABOVE RRDUMn 2.46
PERSONNEL. FDD
EQUIPMENT DESCRIPTION.
V-orV- GR-81
BACKGROUND START 50
BACKGROUND FMri 60
TIME CONSTANT.
10RANGE
10
PAGE .OF.
TIME
4:00 pn
4: 20pm
i:27pm
DEPTH
89.4'
89
8887
8685
84
83
82
81
80
79
78
77
76
75
74
73
72
71
70
69
68
67
COUNTS
70
65
6068
8058
54
47
50
51
65
105
50
35
28
50
48
37
30
30
33
35
27
26
TIME
4:32pn
DEPTH
66 '
65
6463
6261
60
59
58
57
56
55
54
53
52
51
50
49
48
47
46
45
44
43
COUNTS
38
96
127132
7053
56
50
44
43
44
50
57
90
58
44
37
40
100
105
92
69
50
60
TIME
4: 40pm
DEPTH
42 '
41
4039
3837
36
35
34
33
32
31
30
29
28
27
26
25
24
23
22
21
20
19
COUNTS
64
63
6460
5057
67
80
65
66
68
80
93
84
78
74
70
60
92
60
63
57
50
45
TIME
4:50
DEPTH
18'
17
16
15
14
13
12
11
10
9
8
7
6
5
4
3
2
1
COUNTS
50
30
IS
28
9S
33
88
101
110
103
100
94
92
100
90
80
70
71
KASLAND t IOUCXINOINIIK, f.C.
GAMMA RAY LOGGING
WestinghouseBloomington Sites
PROJECT MO 112-3612/3/87
WELL /BORING NO. MU-1 7
FLUID l FVFI 79.2 TOG
FI nin water
GROUND.
Lemon Lane Landfill PERSONNEL__PDD_
at ground level
EQUIPMENT DESCRIPTION.
Keck GR-81
BACKGROUND START.
BACKGROUND END
TIME CONSTANT
RANGE 10
65
65
10
PAGE
TIME
10:45ai
ll:00a
DEPTH
i 98.3'
98
97
96
95
94
93
92
91
9089
88
87
86
85
84
83
82
81
a 80
79
78
77
76
COUNTS
75
75
64
70
68
45
45
45
47
75108
100
86
88
78
80
84
115
110
138
110
80
£5
58
TIME
ll:10a
DEPTH
75'
74
73
72
71
70
69
68
67
6665
64
63
62
61
m 60
59
58
57
56
55
54
53
52
COUNTS
42
38
50
50
40
43
45
54
50
5058
65
90
70
60
67
100
75
60
60
63
80
80
60
TIME
11:20*
DEPTH
51'
50
49
48
47
46
45
44
43
4241
m 40
39
38
37
36
35
34
33
32
31
30
29
28
COUNTS
50
45
60
58
75
90
55
50
60
5051
38
37
44
36
35
37
45
54
83
105
79
50
38
TIME
11:30.
DEPTH
27 '
26
25
24
23
22
21
im 20
19
18ll
16
15
14
13
12
11
10
9
8
7
6
5
4
COUNTS
40
38
32
40
35
46
48
67
53
49tt>
72
64
52
46
45
65
88
93
90
80
77
86
84
KASLANO * KXICKINOINilK, f.C.
GAMMA RAY LOGGING
PROJECT.
WestinghouseBloomington Sites
112-36PROJECT NO..
DATE_I2/3/87_
WELL /BORING NO.
FLUID LEVEI 7 9 -2
MW-12
FI nin waterreference oint
ABOVE GROUND.
SITE. Lemon Lane Landfill
at" grnnnH level
PERSONNEL. FDD
EQUIPMENT DESCRIPTION.
BACKGROUND START.
BACKGROUND END
TIME CONSTANT
RANGE
65
in
10
PAGE .OF.:
TIME DEPTH
3 '
2
1
COUNTS
80
75
74
TIME DEPTH COUNTS TIME DEPTH COUNTS TIME DEPTH COUNTS
•LASIANO l> lOUCKBtOINEIK, *.C.
GAMMA RAY LOGGING
WestinghouseBloomington Projects ,.|TF Lemon Lane Landfill PERSHMNFI
PRQ-IFT-T NO H2-36
niTr 12/3/87
WF| 1 /BORINR NO MW-13
PI inn i FVEI 56.25
niim water
reference point«ASH«k*K*6c!j6c AROVF GROUNn at 8round level
EQUIPMENT DESCRIPT
Keck GR-81
BACKGROUND START
BACKGROUND END
TIMF OnNSTANT
RANfiF 10
ION
62
61
10
PAGE,. .OF.
TIME
12: 45pm
12: 54pm
DEPTH
56.8'56
55
54
53
52
51
50
49
48
47
46
45
44
43
42
41
40
39
38
37
36
35
34
COUNTS
80
97
100
115
125
140
120
90
60
61
58
55
50
52
70
100
95
70
71
96
140
144
101
73
TIME
1 :00pm
DEPTH
33 '32
31
30
29
28
27
26
25
24
23
22
21
20
19
18
17
16
15
14
13
12
11
10
COUNTS
70
77
75
93
94
77
66
70
74
78
86
78
84
98
100
90
95
87
90
103
111
126
122
125
TIME DEPTH
Q '
8
7
6
5
4
3
2
1
COUNTS
i in120
110
100
101
100
80
70
65
TIME DEPTH COUNTS
•LASIAND * BOUCKEMO4MHK, P.C.
GAMMA RAY LOGGING
WestinghousePRDJFCT Bloomington Sites
PROJECT ND H2.3612/3/87DATE.
WELL /BORING NO. MW-14
FLUID LEVEL 95.1 TOC
waterFLUID,reference point
ABOVE GROUND
<;ITF Lemon Lane Landfill PERSONNEL. pnn
EQUIPMENT DESCRIPTION.
Keck GR - 81
BACKGROUND START 55
BACKGROUND END__5JL
TIME CONSTANT U2_
RANGE TO
PAGE .OF.
TIME
1 : 20pm
l:30pm
DEPTH
124.5'
124
123
122
121
120
119
118
117
116
115
114
113
112
111
110
109
108
107
106
105
104
103
102
COUNTS
110
80
57
60
60
50
46
40
38
44
70
110
110
87
57
64
80
78
75
73
66
80
79
68
TIME
l:40pm
DEPTH
101'
100
99
98
97
96
95
94
93
92
91
90
89
88
87
86
85
84
83
82
81
80
79
78
COUNTS
50
47
40
22
25
25
34
30
27
30
37
40
38
50
62
70
54
43
60
73
83
58
51
75
TIME
l:47pm
DEPTH
77'
76
75
74
73
72
71
70
69
68
67
66
65
64
63
62
61
60
59
58
57
56
55
54
COUNTS
65
54
45
38
56
54
76
60
34
17
24
47
34
30
30
35
33
32
28
27
47
70
92
91
TIME
1 :54pm
DEPTH
53 '
52
51
50
49
48
47
46
45
44
43
42
41
40
39
38
37
36
35
34
33
32
31
30
COUNTS
70
46
35
33
31
35
34
30
30
65
54
41
37
56
95
80
50
30
34
37
50
65
64
50
UAILAND * SOUCXINOINIIK, P.C.
GAMMA RAY LOGGING
PROJECT.
WestinghouseBloomington Sites
PROJECT NO. H2-3612/3/87
WELL /BORING NO. MW-14
FLUID LEVEL 95.1 TOC
waterFLUID.reference, point , ,
TXABOVE GROUND _±_i:
Lemon Lane Landfill FDDSITE PERSONNEI
EQUIPMENT DESCRIPTION.
Keck GR - 81
BACKGROUND START.
BACKGROUND END
TIME CONSTANT
RANGE 10
55
58
10
PAGE .OF.
TIME
2: 02pm
DEPTH
29'
28
27
26
25
24
23
22
21
20
19
18
17
16
15
14
13
12
11
10
9
8
7
6
COUNTS
42
58
49
58
65
65
59
57
50
47
45
43
40
42
50
67
75
78
73
70
70
75
7o
60
TIME DEPTH
5'
4
3
2
1
COUNTS
65
63
53
45
40
TIME DEPTH COUNTS TIME DEPTH COUNTS
APPENDIX LL-9A
fi>0
X
APPENDIX LL-9A
CONTINUOUS WATER ELEVATION HYDROGRAPHS
LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
12/05 - 12/19/87
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12/19/87 - 01/05/88
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01/05 - 01/18/88
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01/18 - 02/01/88LEGEND
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
I • 02/01 - 02/14/88
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
02/14 - 02/29/88
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
02/29 - 03/18/88
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
03/18 - 04/06/88
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
04/06 - 04/18/88
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
04/18 - 05/09/88
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LEMON LANE LANDFILLCONTINUOUS WATER ELEVATIONS
05/09 - 05/25/88
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05/26 - 06/14/88
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06/14 - 06/29/88
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APPENDIX LL-9B
APPENDIX LL-9B
STORM-EVENT HYDROGRAPHS
830.00
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
11/24 - 12/01/87
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
12/14 - 12/15/87
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
12/24 - 12/31/87
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
01/16 - 01/20/88
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
01/31 - 02/05/88
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
02/18 - 02/20/88
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03/02 - 03/06/88
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LEMON LANE LANDFILLSTORM EVENT HYDROGRAPHS
06/08 - 06/09/88
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06/16/88
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APPENDIX LL-10
APPENDIX LL-10
LOW FLOW TRACER TEST REPORTSHYDROSCIENCE ASSOCIATES
PRELIMINARY REPORT OF TRACER STUDY:LEMON LANE SITE, BLOOMINGTON, IN
Test I: Low Flow Test
(Hydrosclence Associates, Inc.)
Injection;
The low-flow test was designed to determine travel time and discharge
points of water from the vicinity of the Lemon Lane Landfill under assumed
lowest gradients. Drilling Into the landfill proper was not permitted due to
fear of exacerbating any potential ground-water contamination problem.
Consequently, It was decided to inject the tracer into three drill holes
surrounding the site.
Relying upon the experience of earlier investigators using bromide (Leap
and Ma1, 1986; Murray Rouse and Carpenter, 1981), lithium bromide (LiBr) was
chosen as the tracer compound because of its 1) low toxcicity, 2) high
solubility and 3) proven utility as a tracer because of the ease of detection
of the bromide ion at low concentrations. In addition, it was felt that a
stable, soluble, conservative salt would be best for a low-flow test because
we were not sure a"-priori how long the travel time would be from emplacement
to retrieval and feared that organic dyes might be retarded more than bromide
by clays and organics.
Murray, Rouse and Carpenter (1981) performed a lithium bromide test in a
carbonate system under conditions very similar to the Lemon Lane Site and
envrions. Their tast involved the emplacement of 45 kg of brine containing 25
kg of LiBr (a 56X solution) into a landfill which then was detected at springs
0.5 to 1.5 miles away.
At the Lemon Lane Site 20 gallons of LiBr solution was injected into each
well. This particular amount was chosen because 1) it is about 2.6 times the
amount injected in the referenced paper and because little was known about the
system, this amount was assumed more likely to yield good results than the
amount injected in the Missouri study; 2) the solution is shipped in 30 gallon
containers and two containers (60 gallons) was assumed enough where one
container was not thought sufficient. The solultion had a concentration of
approximately 55X.
After the 20 gallon LiBr spike was either poured into or pumped into each
of the wells, 55 gallons of water was then added to the well to flush the
tracer out of the well and into the formation. This amount of water was equal
to at least two water columns in each w.el1.
Open Hole Depth of Time ofWell Screened Interval Tracer Emplaonent Emplacement
12:26pm - 12:34pm3:22pm - 3:35pm4:24pm - 5:20pm
MW7MW-10MW-1D
Sampl ing
50-60 feet73-86 feet46-56 feet
and Analytical Results:
50 feet73 feet46 feet
Sampling at well and spring sites was begun on October 27, 1987 in order
to obtain background. All times reported hereafter are listed in hours since
midnight October 26-27, the zero time. Injection time is then taken to be
midnight on November 10, 1987 because actual injection times are spread out
over several hours at three wells and this time is convenient without causing
noticeable errors over a span of several days.
Analyses were performed in triplicate by High Performance. Liquid
Chromatography (HPLC) and the results are listed in Appendix I. Appendix II
shows the actual breakthrough curves. Spring discharge data is shown in
Appendix III.
Examination of the breakthrough curves shows peaks as follows:
Time of Peak Time of PeakSampling Point After Zero (hrs) After Injection (hrs)
Crestmont A 374.1 14.1Crestmont B 374.1 14.1Illinois Central 613.1 253.1Quarry 632.3 272.3Urban 361.5 1.5
380.8 20.8Well 11 426.9 66.9Well 8 D 712.8 352.8W?ll 8 S 360.5 >. 0.5
The stream flow data from springs shows two significient rain events on
October 27, 1987 and November 27, 1987. The tracer emplacement and sampling
took place between these peaks and therefore, there is little probability of
high flow influences on the test.
REFERENCES:
Leap, D.I., and Mai, P.A., 1986, Variation of dispersivity with ground-watervelocity in fissured aquifers determined by two-well recirculating tracertests: in Proceedings of Fifth International Symposium on UndergroundWater Tracing, Athens, Greece, Sept. 1986, 19 pp.
Murray, J.P., Rouse, J.V., and Carpenter, A.B., 1981, Groundwatercontamination by sanitary landfill leachate and domestic wastewater incarbonate terrain: Principal source diagnosis, chemical transportcharacteristic and design implications: Water Research, Vol. 15, p.745-757.
LAB ANALYSIS FOR BROMIDE TRACER:WESTINGHOUSE BLOOHINCTON TRACER TEST
The methods outlined by Stetzenbach and Thomson (1983) were used to obtain
bromide concentrations. Sub-ppm levels of bromide could be detected by ion
exchange chromotography using UV detection (190 nm).
Apparatus:
Our HPLC system consisted of a Varian Model 5000 liquid chromatograph, a
Gilson Holochrome variable wavelength detector, a Varian Model 9090 autosampler
equipped with a Valco injector, and a Hewlett-Packard Model 3390A Integrator.
Reagents:
The mobile phase was prepared using AR grade potassium phosphate monobasic
(manufactured by Mallinckrodt) dissolygd JjL glass distilled water. External
standards were prepared using lithium bromide, AR grade, also dissolved in glass
distilled water.
HPLC Procedure:
A Partisil SAX 10 fat ion exchange column (250 by 4.6 mm) purchased from
Phenomenex Company was equilibrated for one hour with the mobile phase flow rate
of 2 ml/Bin. The concentration of the buffer was 0.025 M. This concentration
gave good baseline- resolution for bromide relative to nitrate, which elutes before
it. Lower resolution was obtained with higher concentrations. A 200 pi sample
was injected using the autosampler following column equilibration. Bromide was
detected at 190 nm. Three injections were made per sample. Sample run time was 7
minutes. All samples were run within 28 days of receipt.
Data Analysis:
All data were input into a PC-XT and analyzed using Lotus 1-2-3. Samples
were rerun when the standard error between injections was greater than 10% of the
mean of the injections. Bromide concentration was quantified using external
standards as previously mentioned. To conrirm that the values obtained were
within quality control limits at the 90% confidence level, standards were run with
each set of 100 samples. Verification of the analysis was handled by addition of
spikes to selected samples. Samples were prefiltered using .45 pm filter paper.
Approximately 750 samples were run.
References:
Stetzenbach, K.J. and G.M. Thompson, 1983, Groundwater 21, 36-41.
/
:«/ts
SAMPLE MAflE DATE TINE PPH Br hr
CRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTRONT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTHONT PARKCRESTMNT PARKCRESTRONT PARKCRESTMIT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTMNT PARKCRESTKONT PARK
10/28/8711/03/8711/10/87ll/U/87U/ll/87ll/U/87ll/U/8711/12/8711/12/87W 12/8711/12/8711/12/8711/13/8711/13/8711/13/8711/13/8711/14/8711/15/8711/13/8711/16/8711/16/8711/17/8711/18/8711/19/8711/21/8711/22/8711/23/8711/24/8711/23/8711/26/8711/27/8710/28/8711/03/8711/10/87ll/U/8711/11/87U/ll/8711/11/8711/12/8711/12/8711/12/8711/12/8711/13/8711/13/8711/13/8711/13/8711/14/8711/14/87U/ 15/8711/13/8711/16/8711/16/8711/17/8711/18/87
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tl/D/8711/20/8711/21/8711/22/8711/23/8711/24/87U/23/8711/26/8711/27/87i 1/27/8710/28/8711/06/8711/10/8711/11/8711/11/8711/11/8711/11/8711/12/8711/12/8711/12/8711/12/8711/12/8711/13/87W 13/8711/13/8711/14/8711/14/8711/13/8711/13/8711/13/87U/16/8711/16/8711/17/8711/18/87ll/D/8711/20/8711/21/8711/22/87H/22/8711/23/8711/24/8711/23/8711/26/8711/27/8710/28/8711/03/8711/10/8711/11/8711/11/8711/11/8711/11/8711/12/87It/12/8711/12/8711/12/8711/12/8711/12/8711/13/8711/13/8711/13/87
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10:35 AH11:00 AH
0.0213
0.01250.01520.0177
0.0158
0.03990.0283
0.20260.0428
0.03010.0403
0.07390.03670.03620.01420.0284
0.06210.06710.06310.02440.02370.03420.03410.0484
0.0241
0.03610.0234
0.01360.0246
0.02480.01910.0224
0.01710.0180
0.04031.4977
0.07910.0406.0.0087
0.11320.1345
0.09390.0292
0.03260.0423
0.03430.02410.02180.0160
0.01450.01890.05440.0484
0.03420.0401
0.04920.03880.03680.0314
0.0133
611.7635.3659.46CKO713.4831.4423.)438.5430.7463.1473.)486.3498.1314.3
12.5202.0334. i360.2366.7372.6378.4384.4391.2396.9402. &408.2414.3420.6338.1562.5586.7610.7634.3638.3682.)712.8830.1
10.3202.0334.8360.5366.3372. &378.7384.7391.0397.0402.8408.3414.6420.9426.1439.0450.9463.2472.9486.7498.45(4.6339.0
Ib
WELL 8SUELL 8SHELL BSUEIL BSWLL8SUEIL BSHELL BSUELL BS
11/11/8711/20/8711/21/8711/23/8711/23/8711/24/8711/23/8712/01/87
10:30 Afl10:43 AH10:54 Afl10:33 W110:37 M10:58 AN4:12PH
10:40 Afl
0.01130.00810.01120.01040.01380.00)90.00130.0161
562.5586.8610.)658.6658.6683.0712.2850.7
APPENDIX II
Breakthrough Curves
PPM Br1.000-r
0.500--
0.000
CRESTMONT A
to+ + + +
100 200 300 400 500
TIME (hrs)
600 700 800
CO
PPM Br1.000
0.500--
0.000
CRESTMONT B
H *-
u
0 100 200 300 400 500 600 700 800
TIME (hrs)
PPM Br
1.000T
0.500 +
0.000
DETMER
0 100 200 300 400 500
~IME (hrs)
600 700 800
oCM
PPM Br
5-
4- -
1 -•
0
ILL Central
1
100 200 300 400 500 600 700 800
TIME (hrs)
r\j
PPM Br1.000
0.500-
1.000
PACKIIIG HOUSE RD
0 100 200 300 400 500
TIME (his)
600 700 800t
Mvj
PPM Br1.000
0.500-- PUMPING STATION
0.000 l1
0 100 200 300a
400 500
TIME (hrs)
600 700 800
enCM
PPM Br
6T
c _.
4..
3- -
2 - -
1 -
0
QUARRY
I T^T i I
0 100 200 300 400 500 600
TIME (hrs)
700 800
*
(
r\i
PPM Br1.000
0.500-
0.000
SNODDY A
-0-0 O
0 t 100 200 300 400 500 600 700 800f
FIME (hrs)
inCM
PPM Br1.000
0.500--
0.000
SNODDY B
0. 100 200 300 400 500
TIME (hrs)
600 700 800
10
PPM Br1.000
0.500-
0.000
STONY EAST
0 100 200 300 400 500 600
TIME (hrs)
700 800
csi
PPM Br1.000
0.500 STONY WEST A
0.000 -I 1 1 1 • i 1-0 100 200 300 400 500
TIME (hrs)
600 800
COCM
PPM Br1.000
0.500-
0.000
STONY WEST B
•o— o—o.
I- 0--0
0 100 200 300 400 500 600 700 800
TIME (hrs)
enCM
PPM Br1.000
0.500
0.000400 500
TIME (hrs)
600 700 800
oro
PPM Br1.000
0.500-
0.000-
WELL 11
V- I ^O-A-Q-U
0 100 200 300 400 500 600 700 800
TIME (hrs)
ro
PPM
1.000
0.500
0.000 -0
WELL 5
100 200 300 400 500
TIME (hrs)
GOO 700 800 900
roro
PPM Br
3-r
24-
U
04*
WELL 8D
^0 100 200?
300 400 500 600
TIME (hrs)
\800 900
CO
PPM Br
1.000T
0.500-
0.000
WELL 8S
0 100 200 .500 400 500 600 700 800 900
TIME (hrs)
(
APPENDIX III
Spring Discharge Data
35
CRESTMONT PARK ANot able to install weir due to rocky stream bed
• CRESTMONT PARK B(Zero Reading - 1.377, 45° Weir)
(H) (Q)Date Gauge Reading Gauge-Zero Flow(cfs) Flow (gpm)
10-05-87 1 . 4 2 3 0 : 0 4 6 ' o.oooe 0.2710-28-87 1.453 0.069 0.0016 0.72
(zero - 1.384)
DETMER SPRING(Zero Reading « 1.365, 90° Weir)
(H) (Q)Date Gauge Reading Gauge-Zero Flow (cfs) Flow (gpro)
10-08-87 1 . 7 4 3 0 7 3 7 5 0 . 2 1 5 9 6 . 6 410-15-87 1.628 0.263 0.087 39.0210-23-87 1.654 0.289 0.110 49.3910-28-87 1.860 ILA95 0.422 189.6411-06-87 1.705 0.340 0.165 74.1511-13-87 1.694 0.329 0.152 68.3011-27-87 1.877 0.512 0.460 206.54
ILLINOIS CENTRAL SPRING(Zero Reading - 1.377, 45° Weir)
(H) (Q)Date Gauge Reading Gauge-Zero Flow (cfs) Flow (gpm)
10-08-87 1.472 O55 O T U O l 1 . 3 511-05-87 - 0.178* 0.033 14.8211-27-87 No reading, Weir under water
*90° Weir
PACKING HOUSE ROAD SPRING(Zero Reading « 1.378, 90° Weir)
(H) (Q)Date Gauge Reading Gauge-Zero Flow (cfs) Flow (gpm)
10-08-87 1.495 07TT7 OTT 5.1510-15-87 1.512 0.134 0.016 7.2310-23-87 1.492 0.114 0.010 • 4.8310-28-87 1.574 0.196- 0.042 (high) 18.7111-05-87 1.461 0.083 0.005 2.1811-13-87 1.505 0.127 0.014 6.3211-27-87 1.630 0.252 0.078 (high) 35.07
36
Date10-08-8710-15-8710-23-8710-27-8711-05-8711-14-8711-27-87
QUARRY SPkiNG(Zero Reading « 1.370, 90° Weir)
Gauge Reading1.5661.6071.5801.7751.6061.6201.831
(H)Gauge-Zero
0.1960.2370.2100.4050.2360.2500.461
(Q)Flow (cfs)
0.0670.0500.256 (high)0.0660.0070.354 (high)
Flow (gpm)TOb30.0822.45
114.9429.6334.57
158.95
DateTO-09-8710-12-8710-15-8710-23-8710-28-8711-05-8711-13-8711-27-87
SNOODY SPRING A(Zero Reading - 1.396, 45" Weir)
Gauge-Reading1.4521.4821.4221.4141.5091.4051.4251.641
(H)Gauge-ZeroO5S0.0860.026
j.130.0090.0290.245
(Q)Flow (cfs)
9.4 x icr;*2.7 x 10-31.4 x 10-J5.6 x 10-55.3 x 10-31.0 x 10-51.8 x TO'4
Flow (gpra)0.421.220.060.022.400.0050.08
0.036 (high) 16.33
DateTTJ-09 8710-12-8710-15-8710-23-8710-28-8711-05-8711-13-8711-27-87
SHODDY SPRING B(Zero Reading • 1.597, 90°
Gau<,e-Read1ng1.7791.7991.7651.7671.8031.7431.7281.818
(H)Gauge-Zero
7BZ0.2020.1680.1700.2060.1490.1310.221
Weir)
(Q)Flow (cfs)O3S0.0450.0280.0320.0470.0210.0150.056
Flow (gpm)o* (gT575520.17 (high)12.7314.3221J9 (high)9.436.83
25.26 (high)
37
Date10-12-87
STONY SPRING EAST(Used Marsh/McBurney Meter)
Reading (ft/sec)channel widthwater depth
17 inches0.2 feet
17
11-06-87
11-13-87
10-28-87
center
3" from N side3" from S side
center
3" from N side3" from S side
middle
3" from N side3" from S side
center
ft/sec
ft/sec• 0.80
0.150.150.20
(negative reading)0.0090.1
.08
.30
Date10-12-87
10-15-87
11-06-87
11-13-87
STONY SPRING WEST(Used Marsh/McBurney Meter)
Reading (ft/sec)channel widthwater depth
J1
27"
Q-- 0** *. 2
• 27 Inches•0.2 feet
EJ,/ 9" from W side$ 18" from W sidey. j 9" from E side* 12" from E side
12" from W side
ft/sec
.37
.51
.40
.47
.50
ft/seccenter « 0.10
6" from E side - .086" from W side - .10
9" from W side « .05center - 0.20
9" from E side - 0.10
9" from W side - 0.17center » 0.25
9" from W side » 0.18
10-28-87 center « 0.416" from E side - 0.40
38
URBAN1
(Zero Reading <
DateTO-OB-8710-15-8710-23-8710-28-8711-05-8711-14-8711-27-87
Gauge-Reading1.4101.4251.4151.4341.4141.4281.450
Ga
S SPRING• 1.377, 45° Weir)
(H)e- Zero
0.0480.0380.0570.0370.0510.073
(Q)Flow (cfs)Z.5 x lO'46.4 x 10-43.6 x 10-49.8 x 10-43.3 x lO.A7.4 x 10-'1.8 x 10-3
Flow (gpm)0.110.290.160.440.150.330.81
(high)
(high)
PRELIMINARY REPORT OF TRACER STUDY: LEMON LANE LANDFILL
Bloomington, Indiana
(Hydroscience Associates, Inc.)
Water Sample Collection
Water samples were collected in new bottles after thorough rinsing
with the water sampled. All samples were filtered through a ^5 micron
filter prior to analysis for bromide. The specific conductance values were
measured in the field with a Cole Parmer Kodel 1(070 specific conductance
meter. The unit of measurement is the m crosier-en which is the
international equivalent of the microrohos. Data tables for specific
conductance and graphs of specific conductance with times are presented in
Appendices ^ and 5, respectively.
Discharge
Discharge measurements were taken using ^5° and 90° V-notched weirs
except for Stony Spring East and Stony Spring West A and B. A Marsh-
KcBurney flow meter was used because of the rock botton: of the channels.
The low flow measurements could not be accurately measured with this meter,
therefore, the data is not included in this report. The following flow
calibration equations were used to calculate the discharge:
(1) 93° weir Q in cfsQ - 2. 5 H2'5 H in ft
(?) U5° weir Q in cfsQ - 2.35 H2'143 H in ft
2 1 cfs - H^9 gpr
Discharge data are presented in Appendix 3 of this report.
Appendix 4
Specific Conductance Data
Lemon Lane Tracer Study
SPECIFIC CONDUCTANCE VALUES FOR WEST IN5HOUSE TRACER PROJECT
well
phsnasnbdimstestwaatwbquliecr pacr pburps
date:t iKe:SpC:
11/03 '6 pn.
8364846576606625733988008078861077675187
11/106 pm
719422599603613515402744793712978735185
11/1112 am
759488607589609526399737798808982710195
11/116 at
750554616630613532400740802757;995720187
11/1112 pc.
726485596605594511392717780795977720187
11/116 pm
8203986056516315324057848118551056763176
datetineSpC:
phsnasnbdtnstestwastwbquliecr pacr pburps
11/1212 am
726498609616570528389693739803939730196
11/126 ani
8386466646596175384057778198431103799178
11/1212 pa
8014006306346125614207387956821050770182
11/126 pa
7964306506816585554317928248891106813168
11/1312 at
79650262364561152439278076285^1061759195
11/136 am
80557564267763756041779984213471125835172
backarounc data
LOCATION KEY:
ph Packing House Roadsna Snoddy Asnb Snoddy Bdtn Detmerste Stony Springs Eaststwa Stony Springs Weststwb Stony Springs West
qu Quarrylie Illinois Centralcr pa Crestmont Park Acr pb Crestiiont Park Bur Urbanps Futplng Station
11/2012 pa
91356174775773763748791895910051218969225
11/2112 pit
932998791792714653496913982
107512931051765
11/2212 pa
808555672673671564435837870907
1111875504
11/2312 pa
8164816526076655684568048736781055846764
11/2412 pa
818499689641692542440812889880
1041872232
11/2512 pa
573501312202461260436645768179836489550
datet lae ;SpC:
phsnasnbdtnstestwastwbquliecr pacr pburps
date: 11/25 11/26 11/27tine: 12 pm 12 pa 12 paSpC:
ph 573 687 705sna 501 560 614snb 312 535 557dim 202 389 466ste 461 591 615stwa 260 382 378stwb 436 405 372qu 645 753 586lie 768 540 555cr pa 179 476 631cr pb 836 1147 1115ur 469 642 710ps 530 695 661
snasnb
date;tineSpC:
stestwastwbquliecr pacr pburps
date:tl»e :SpC:
phsnasnbdt»stestwastwbquliecr pacr pburps
11/1312 pn
8155556556566555604368058418721112815328
11/136 pn
8144696536586635484377828418931088795219
11/1*12 at
8235516516626455564267908308871082806435
1 1 / 1 *6 ate
8485696857036735734376368949431144870192
11/146 pit.
7975136656916555494427828358941033820185
11/156 at
7864956636496495424167888648981068814618
11/156 pt
8165016406686615454228008528831078830192
11/166 am
850488690711706573450841902944
1145177192
11/166 p&
93557679378577964757282299310551268968214
11/1712 pm
8325206836567055864748058906961125879388
11/1812 p*
8645946806706885884848559288461131882201
11/1912 pa
8475156876866865674378529309111155904797
Appendix 5
Specific Cor.ductar.ee vs. Tire Graphs for
Lemon Lane Tracer Study
f]
>*clf ic
C
ork
rt u
r t*
r»<
CT K
ovi s »
rn tl v
)
Mi
C
1.6 ~
1.1 -
1 -
0.8 -
0.8 -
0.7 -
0.6 -
0.6 -
0.4 -
0.3 -
0.3 -
0.1 -
0 -
\\
, v ___^,
3 E f E V! ' ^ 4 ; + \
"" , h r \ / \ \< r *I ! \ \/ \ y/1 ' / \ / •*• > A
,j 1 A \/A '' •'" \ / \/ \// V I / I / • V i:' * I ) i A y •*• *
t- -f* -kf'*v^+*^ ' -»-4 •*— *"^
> i i i i i i t i i i i i i i i i10 12 14 16 18 30 32 E4 36 SI
Urban?November d*:r
Pumping
tuC
3 C
S:£ 5t 60 £
£~cac
0.4 -
0.3 -
0.2 -
0.1 -
0 -
V
10 IS 14 16 1C SOi 1 l
32 24
Stonr Ef t ? :November
-t- S'.ony !»>!-. A <• S-.onv ¥e»: B
c«*.' '0 ,3C
CU
0
6K
10 12 14 16 18 20 22 24
Kovembrr d»tcBoy?t + Snoddv A c Snoddr B
26i
28
ft0Cc „V _
Sje3?
<7or»
rtO
Xlf
lftT
*tV. W
liftC.
i.o -
1.4 -
1.3 -
1.2 -
1.1 -
I / ^
^ (i. * X v— -t-^-*' \ft •*• f A.' ^F 1 ' ' V| ^ ""T p j *" ^
v^-
i- 4-^' r v' A ^ \ ^~+ ) 1 Pi E V S \ \
°'* ~h r^C CB ' -&-B' \ S* \ C X
0.8 - F^C K ' \ / \ / \
V V \o.e - \0 . 6 - i . \
0.4 -I \
0.3 -
0.2 -
0.,-
I i 1 ! 1 i i 1 i i ; 1 f 1 1 (
10 IS 14 16 16 20 23 24
/--,i
/v /V
D
//
\/Vb
1 1 i
2C »
NovemberD CrcsTnon* A * Crrv.monT B
ce „*•' *
t,
C.K
D QuarryNovember df.eT lllmoi? C<n*.r»l
FIGURE LL-I
LEGEND
O MONITORING WELL
A. SPRING
O TRACER SAMPLINGLOCATION
O TRACER INJECTIONLOCATION
LEMON LANE LANDFILL
LOW FLOW TRACER INJECTIONAND SAMPLING LOCATIONS
NOVEMBER 10-24, 1987
y_^y > •1AMAMO t »O
J ~T !'*<>'**"« » C
IX LL-11
APPENDIX LL-11
LOW FLOW TRACER TEST MEMORANDUMBLASLAND & BOUCK ENGINEERS, P.C.
To: ™** Date: 2 /1 /88
From: J-L- Jenkins Fj|e No . 112.36 13
DA- Low Flow Tracer Test -»-. W. SannerWW. r~ u; I _- I..G.W. Lee, Jr.
T.E. GassN.E. CenskyC.S. SanfordP.O. DuBois
Tuesday, November 10, 1987, Blasland £ Bouck Engineers and Hydroscience,Associates, Inc., began a two-week low flow ground-water tracer test at theLemon Lane Landfill. Bloomington. Indiana. The tracer test was a task of theSupplemental Hydrogeologic Investigation of the Lemon Lane Landfill Siteperformed by Blasland 6 Bouck Engineers for Westinghouse ElectricCorporation. Hydroscience Associates, Inc., designed the tracer test andBlafland £ Bouck Engineers provided technical assistance and support.
Pre-Tracer Injection Activities
Two weeks prior to the tracer injection, Blasland 6 Bouck Engineersperformed two rounds of ground-water elevation measurements and obtainedground-water samples from Wells MW-8D, MW-8S. MW-5 and MW-11 (FigureLL-1). These wells were selected as sampling locations by HydroscienceAssociates, Inc., as potential upgradient and downgradient wells. Wellpurging and ground-water sampling was performed with a Keck portablesubmersible pump. Ground-water sampling procedures outlined in AppendixI, Ground Water Tracer Test Protocols of the Lemon Lane SupplementalHydrogeologic Investigation Plan, June 1987 were followed. Decontaminationprocedures outlined in the Lemon Lane Landfill Supplemental HydrogeologicInvestigation Plan, June 1967, were followed before emplacing the submersiblepump in each well. Also during this time period, Hydroscience Associates,Inc., sampled and performed discharge measurements on 13 springs in thevicinity of the Lemon Lane Landfill (Table LL-1. Figure LL-1). Thesesprings were selected by Hydroscience Associates. Inc., from numerouspotential locations in the area based upon flow observed during the low flowperiod. The ground-water and spring, samples end discharge and elevationmeasurements were used to obtain background information on the wells andsprings that were sampled during the tracer test.
Tracer Injection Activities
Dr. Darrell Leap and Dr. Noel Krothe of Hydroscience Associates, Inc., andNancy Gensky, Peter DuBois and Josh Jenkins of Blasland 6 BouckEngineers, performed the tracer injection on November 10th. William Sannerof Westinghouse Electric Corporation and Dr. Richard Powell of GeosciencesResearch Associates, representing the USEPA, were also present to observeand assist in the tracer injection.
Memo to: FilesFebruary 1, 1988Page 2
The tracer selected by Hydroscience Associates, Inc., was a 551 lithiumbromide brine. The tracer was injected in Wells MW-7, MW-10 and MW-1D(Figure LL-1) by pouring the brine down 2-inch PVC pipe to a predetermineddepth in each well. Hydroscience Associates, Inc.. selected the wells anddepths of injection for each well based upon core analyses, caliper loggingand packer testing results. The times of injection and the depths of injectionwere:
Well Injection Time Depth Below Surface
MW-7 12:26 p.m. 50' Sflfti'
MW-10 3:22 p.m. 73' 8'*-'3
MW-1D 4:21 p.m. 47' 808.60
Twenty gallons of brine was poured into each well. Immediately after pouringin the brine, 55 gallons of control water obtained from a fire hydrant onLemon Lane was poured in the top of the well to flush the tracer into theformation.
Two shallow wells (one upgradient and one downgradient), two deep wells(also one upgradient and one downgradient) and 13 spring locations in thevicinity of the Lemon Lane Landfill (Table LL-1, Figure LL-1) were selectedby Hydroscience Associates, Inc., as sampling locations.
Post-Tracer Injection Activities
Ground-water and surface water samples were obtained approximately everysix hours starting Tuesday, November 10, 1987 at 6:00 p.m. through 6:00p.m. Friday, November 13, 1987. From 6:00 p.m. Friday, November 13, 1987through 6:00 p.m. Monday, November 16, 1987, ground-water and surfacewater samples were obtained approximately every 12 hours. From November17, 1967 through November 24, 1987, ground-water and surface water sampleswere obtained daily at about 10:00 a.m.
The methodology for purging the wells and obtaining ground water sampleswas:
Weil Sampling/Purging Device
V.V.-8S Stainless steel bailer
V.V.-8D Keck portable submersible pumpand stainless steel bailer
MW-5 Hydrostar Pump
MVV-11 Franklin 10 gpm submersible pump
Memo to: FilesFebruary 1. 1988Page 3
All sampling and purging devices were dedicated during the two-weeksampling period. The use of dedicated sampling devices precluded the needfor decontamination procedures that would have been performed if a samplingdevice was used in more than one well.
On at least two occasions, a dedicated stainless steel bailer was used to purgeand sample MW-8D because the Keck submersible pump froze up.
Ground-water elevation measurements were taken periodically during thesamplings in conjunction with pH, temperature and conductivity measurements.
Spring sampling was performed as outlined in Appendix H, Surface Wate*.Sampling Protocol of the Lemon Lane Landfill Supplemental HydrogeologicInvestigation Plan, June 1987. An additional round of dischargemeasurements were taken during the two-week sampling period.
Tracer Analysis
All water samples were shipped to Purdue University, where they wereanalyzed by Hydroscience personnel for bromide using a High PerformanceLiquid Chromatograph (HPLC). The HPLC is capable of detecting bromideconcentrations of almost one-hundredth of a part per million. Results of thebromide analyses are given in Appendix A. It is evident that break-throughoccurred in Quarry Spring and Illinois Central Spring and possibly inCrestmont A and B and Urban's Spring.
Purge Water Disposal
Well purge water from all sampling events was temporarily stored in 55 galkdrums at the well site and later transferred to a 2,500 gallon holding tank atthe Westinghouse Interim Storage Facility. A grab sample of the compositepurge water from the 2,500 gallon holding tank was sent to EMS Laboratoriesin Indianapolis, Indiana for PCB analysis. The results were negative.Therefore, the purge water will be disposed of at the adjacent tertiary lagoonof the Winston Thomas Facility.
/mey
TABLE LL-1
LOW-FLOW TRACER TEST SAMPLING LOCATIONS
LEMON LANE LANDFILL
Wells
MW-8S
MW-BD
MW-5
MW-11
Springs
Quarry Spring
Illinois Central Spring
Urban's Spring
Packing House Spring
Snoddy SpringsLocation ALocation B
Crestmont Park SpringsLocation ALocation B
Detmer Spring
Stoney Spring East
Stoney Springs West,Location A
Stoney Springs West,Location BPumping Station Spring
APPENDIX A
TRACER ANALYSES RESULTS
PPM Br
1.000T
0.500 -I-
0.000
CRESTMONTA
—0&-00
°
+ + -I- +
\-f
100 200 300 400 500 600 700 800
TIME (hrs)
CO
PPM Br1.000
0.500-
0.000
CRESTMONT B
IF o-
O
u
0 100 200 300 400 500 600 700 800
TIME (hrs)
PPM Br
1.000T
0.500--
0.000
DETMER
0 100 200 300 400 500
~IME (hrs)
600 700 800
oCM
PPM
6T
0
/v\
ILL Central / ^
o
'
o
on 0
" 1 1 1 ~ I *f "'"*---- '• - 1 I 1
o\1
D 100 200 300 400 500 600 700 8C
TIME (hrs)
PPM Br1.000
0.500-
1.000o-
0
PACKIIIG HOUSE RD
1 00 200 300 400 500
TIME (his)
603 700 800t
PPM Br1,000
0.500-- PUMPING STATION
0.000 /s + +0 100 200 300 400 500 600
TIME (hrs)
700 800
CO
PPM Br
G T
54
44-
24-
00
QUARRY
100 200 300 °400 500 600
TIME (hrs)
700 800
*
PPM Br1.000
0.500-
0.0000
SNODDY A
_-.q^rrr=r-T:
100 200 300 400 500 600 700 800f
TIME (hrs)
( (
inCM
PPM Br
1.000
0.500-- SNODDY B
<X>n
0.000 -I-,.
100 200 300 C400 500
TIME (hrs)
-h -I-600 700 800
(O
PPM Br1.000
0.500 4 STONY EAST
0.000 I 1 -0 100 200
I™ -I—300 400 500 600
TIME (hrs)
700 800
CM
PPM Br1.000
0.500-
0.0000
STONY WEST A
100 200 300 400 500
TIME (hrs)
600 700 800
00<\J
PPM Br1.000
0.500-
0.000
STONY WEST
0 100 200 300 400 500
TIME (hrs)
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o>CM
PPM1.000
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0.000-0 100 200 300 "400 500
TIME (hra)
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oro
PPM Br1.000
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0.000
WELL 11
0 100 200 300 400 500 600 700 800
TIME (hrs)
(
PPM Dr
1.000 T
0.500-
0.000 O--
WELL 5
0 100 200
AI'-.T I
300 400 500
TIME (hrs)
GOO 700 800 900
COro
PPM Br
24-
00
WELL 8D
100 200 300 400 500 600 700
TIME (hrs)
^800 900
r
CO
PPM Br
1.000 T
0.500-
0.000
WELL as
oo^oc
400 500
TIME (hrs)
600 700 800 900
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FIGURE LL-I
LEGEND
O MONITORING WLLL
A SPRING
Q T R A C E R SAMPLINGI OCATION
(J TRACER INJICTIONLOCATION
IEMON LANE
LOW FLOW TRACER INJECTIONAND SAMPLING LOCATIONS
NOVEMBER 10-24, 1987
APPENDIX LL-12
3mT.
'
•1'3| IK
APPENDIX LL-12
HIGH FLOW TRACER TEST,LEMON LANE LANDFILL, BLOOMINGTON INDIANA
WESTINGHOUSE ENVIRONMENTAL AND GEOTECHNICAL SERVICES. INC.
HIGH FLOW TRACER TESTLEMON LANE
BLOOMINGTON, INDIANA
Prepared for:
Westinghouse Electric CorporationEnvironmental Systems & Services Division
Pittsburgh, Pennsylvania 15220
Prepared by:
Westinghouse Environmental and Geotechnical Services, Inc.Post Office Box 1308
Gary, North Carolina 27512
September 1989
Section No,
1
2
3
3.1
3.2
3.3
3.4
3.5
4
FIGURES
TABLES
APPENDIX
TABLE OF CONTENTS
Title
INTRODUCTION
METHODOLOGY
RESULTS
DYE DETECTION - FB28
DYE DETECTION - AY73
DYE DETECTION - DY96
BROMIDE DETECTION
DATA EVALUATION
DESCRIPTION OF HYDROGEOLOGY
Page No.
1
1
4
4
4
5
12
16
19
1.0 INTRODUCTION
This report is being submitted in fulfillment of Task 1.9
of the Lemon Lane Landfill Supplemental Hydrogeologic
Investigation Plan. W and the other Consent Decree parties
mutually agreed that the development of an on-site monitoring
program as specified in P74a of the Consent Decree could not be
achieved utilizing the data base available in late 1985,
consequently W agreed to perform a supplemental hydrogeologic
investigation which included conducting a tracer test. This
report describes the methodology and results of a high flowt
tracer test conducted at the site from May to July 1989. The
report also presents a description of the hydrogeology of the
site and surrounding area based on an evaluation of the test
results.
2.0 METHODOLOGY
During the spring of 1988 the high flow dye trace was
attempted but due to drought conditions it was postponed until
the spring of 1989. During the period from May 26 through July
22, 1989 the high flow tracer test was conducted at Lemon Lane
Landfill. The hydrologic criteria for determining that the high
flow conditions were occurring were as follows:
(1) The well MW-7 would have a water level of 828' amsl•
or above. The water level at the time of injection
was 833.92' amsl.
-1-
(2) Quarry Spring flow would be in excess of 200 gpm.
Quarry Spring was measured at 747 gpm 24 hours prior
to injection and 1298 gpm 6 hours after injection.
(3) Hinkle Spring would be flowing. It was flowing 20
gpm 24 hours prior to injection.
(4) Sinking Creek swallet would be ponded. It was ponded
5 hours prior to injection.
Tracers were injected on May 26, 1989 in three wells near the
capped area of the landfill as shown on Figure 1. In well MW-7,
a dye known as FB28 (optical brightener) was injected along with
40 gal of lithium bromide (Br-) between 1100 and 1130 hours. In
well MW-10, a dye known as AY73 (fluorescein) was injected along
with 40 gal of Br- between 1300 and 1330 hours. In well MW-1S,
a dye known as DY96 (direct yellow) was injected along with 40
gal of Br- between 1400 and 1630 hours.
Thirty-three stations and five (5) wells were monitored
for the dyes and Br-. Table 1 lists the stations by types.
Figure 2 shows the location of all but four of the stations and
their relation to Lemon Lane Landfill. The four stations which
are located outside the area illustrated by Figure 2 are the
Kirby Road, Sinking Creek, Clear Creek at Hillside, and Weimer
Road stations. The wells that were monitored were 8S, 8D, MW-6,
MW-11 and MW-5 and their locations are shown on Figure 1.
-2-
Initial detectors were put in place at all stations on May
25, 1989 between 1300 and 1800 hours. After tracer injection,
the following stations were monitored every two hours from 1800
hours, May 26, 1989 to 0600, hours May 27, 1989: Crestmont,
Slaughter House, PH Road, Snoddy A & B, Hinkle, ICG-1, ICG-2,
ICG-3, ICG-6, Urban, Quarry, Illinois Central Spring, 7th &
Adams, 17th St., and Pumping Station. The other stations and
the monitoring wells were monitored every 6 hours from 0200
hours, May 26, 1989 to 1800 hours, May 28, 1989. From May 29,
1989 to June 2, 1989 all the stations were monitored daily
between 0800 and 1200 hours. From June 9, 1989 to July 22, 1989
the stations were monitored weekly. Exact time of monitoring
for each station is tabulated in the appendix.
The dyes FB28 and DY96 were monitored with a cotton wad
suspended in the water. The cotton was then collected, washed
and inspected under an ultraviolet light. Presence of FB28 was
indicated by a blue fluorescence and presence of DY96 was
indicated by a yellow fluorescence. If both dyes were present
the cotton would fluoresce white. The dye AY73 was monitored by
suspending a screen packet of activated charcoal in the water.
Upon collection, the charcoal was emptied into a jar and an
elutriating solution of alcohol and potassium hydroxide was
poured on it. If AY73 was present, a green layer would form in•
the elutriant solution above the charcoal. Bromide was
monitored by collecting a grab sample of the water, filtering
-3-
it, and analyzing the filtrate by ion chromatograph. Bromide
analysis was conducted at the I.U. Department of Geology with a
Dionex 4500 ion chromatograph and Spectra Physics 4270
integrator. Specific conductance of the bromides samples was
measured in the field laboratory immediately after filtering.
3.0 RESULTS
3.1 Dye Detection - FB28
The dye FB28 was initially detected with a very strong
positive on the first set of recovered samples (6 hours after
injection) at Illinois Central Spring and Quarry Spring.
Subsequent samples throughout the test continued to show very
strong positives for these two stations.
FB28 was also detected with a very strong positive on July
7, 1989 at Urban Spring. The last two samples (July 13, 1989
and July 22, 1989) also had strong positives for FB28 at Urban
Spring. FB28 was not detected at any other stations.
3.2 Dve Detection - AY73
The dye AY73 was initially detected about 16 hours after
injection at the Edward Pelfree well located about 800'
northwest of the injection well, MW-10. AY73 was next detected
at Illinois Central Spring and Quarry Spring with very strong
visual positives on June 30, 1989. Subsequent samples continued
to show strong positives throughout the test at these two
stations.
-4-
AY73 apparently began to show up at other various springs
and then, following a heavy rain on July 12, all stations showed
a visual green positive. However, the color of the elutriant
was not typical of AY73 and it was decided to submit the samples
to a laboratory for a spectrofluorcphotometer scan to confirm
the absence or presence of the dye.
The results of the laboratory analysis indicated that the
groundwater in the area contained other organic chemicals which
interfered with the detection of AY73 and rendered positive
visual determination of the dye impossible. The laboratory
analysis also revealed background concentrations of AY73 present
in some samples taken in March, 1988.
After additional samples were submitted to the laboratory,
detection of AY73 could be made for 11 springs and/or primary
spring stations. At 16 other primary stations, AY73 was judged
possibly to be present but because of interference from other
chemicals, definite detection was not possible. At only one
station, 17th Street Spring, was there definitely no indication
of the dye. Dye arrival at each individual station could not be
determined as not all of the collected samples were analyzed in
the lab.
3.3 Dve Detection - DY96
For some unknown reason, DY96 was never detected on the
cotton wads. This may be due to the fact that the injection
well was on a "tight" fracture and the dye release was so
-5-
gradual it never adsorbed onto the cotton in detectable
concentrations. Very little is known about the reaction of DY96
with other chemicals present in the groundwater that might have
interfered with the dye's adsorptive capabilities.
The dye is also adsorbed onto the activated charcoal, .
although it does not elutriate visibly. During the laboratory
spectroflurophotometer scans the dye was definitely at the
following stations: Snoddy A & B, Illinois Central Spring,
ICG-3, WS-2, Sinking Creek, and Stouts Creek West. The
detection of DY96 at Stout's Creek West appears to indicate that
one or more unmonitored springs labelled W-2, W-3 and W-5 may
possibly be receiving groundwater flow from Lemon Lane also.
3.4 Bromide Detection
Background bromide samples for all stations were taken on
April 21, 1989 and the results are listed in the Appendix. High
background concentrations were discovered in ICG-2 and ICG-3 and
so bromides were not analysed for these two stations during the
test. The high concentrations were probably due to the
proximity of the county road department's salt stockpile.
Corresponding to the initial appearance of FB28 at Illinois
Central and Quarry Springs, high Br- concentrations were also
detected. Illinois Central and Quarry had peak concentrations
of 8.7 and 10.5 ppm Br- respectively compared to background
concentrations of 0.116 and 0 ppm.
-6-
The following stations had Br- concentrations 3 or more times
above background and are considered likely traces:
1. Illinois Central Br. at Allen
2. Clear Creek
3. Weimer Road
4. Illinois Central Sp.
5. Quarry Sp.
6. ICG-1
7. Urban
8. 7th & Adams
9. Cascade Br.
10. Pelfree Well
11. Sargent Well
12. MW-8S
The Sargent well is located 600' north of MW-1S and bromides
were detected there on 6 samples.
The following stations had Br- concentrations ranging from
1.57 to 2.5 times background concentrations and are considered
possible traces:
1. Sinking Creek
2. ByPass 37
3. Crestmont Sp.
4. Detmer B
5. WS-2
6. Pumping Station
-7-
The other stations did not have bromide peaks.
The tables containing bromide results along with associated
time, specific conductivity, and flow values are included in the
appendix. Also included in the appendix are the graphs of these
values. In most cases an expanded graph of the first 200 hours
is also included for clarity.
3.5 Data Evaluation
Table 2 is a matrix of results. Each tracer is listed for
the primary stations along with the conclusion of whether it was
likely detected, possibly detected, not detected or the result
was inconclusive. The fifth column is an evaluation of the
station's connection to Lemon Lane. The sixth column lists the
time to the first bromide peak in hours following injection.
Zero hour was chosen for convenience as 1200 hours May 26,
1989. This convention is followed for all tables and graphs.
Based on the results of the tracer test, it is concluded
that 11 primary stations are likely connected, 11 primary
stations are possibly connected, 5 primary stations are
inconclusive as to their connection, and one station, 17th
Street Spring is not connected. It should be noted that the
five primary stations that were determined inconclusive had AY73
possibly detected there but, in the absence of any corroborating
tracer and due to the background and/or background interference
of AY73 a positive determination of their connection is not
possible at this time.
-8-
Using the straight line distance from the landfill to the
monitoring stations, approximate flow velocity for the bromide
was calculated. These range from as low as 3.5 ft/hr. to as
much as 615 ft/hr. In actuality, velocity may be even higher,
since the first samples were taken about 6 hours after the
tracers were injected in MW-7. By that time the FB28 and Br-
was already present at Illinois Central and Quarry Springs.
These velocities are in accordance with what other investigators
have reported from their tracer studies in other areas.
/
4.0 DESCRIPTION OF HYDROGEOLOGY
Figure 3 is adapted from Gunn (1985) and shows a
conceptual model for flow in a karst conduit-flow dominated
aquifer. It is applicable to Lemon Lane with some
modifications. There is no non-limestone caprock at Lemon Lane
so rainfall enters the system by either diffuse autogenic
recharge (seepage through the soil around the uncapped portion
of the sinkhole) or concentrated autogenic recharge (flow into a
sinkhole). Flow which enters a sinkhole is carried via vertical
shaft flow into the main lateral conduits. Flow which seeps
through the soil is first integrated in the "sub-cutaneous"
zone. This zone is the upper 30' or so of the limestone bedrock
which is highly fissured. Water entering this zone either
continues to percolate downward as diffuse vadose seepage or is
integrated into a network of smaller conduits termed vadose
-9-
flows. This network of smaller conduits is the tributary system
to the main lateral conduits which conveys the water to the
discharge outlets or springs, analogous to a river basin's
tributaries combining to form a major river.
The situation at Lemon Lane also differs from the
conceptual model in Figure 3 in that Lemon Lane is at or near
the headward or starting point for the main lateral conduits.
Drainage from the sub-cutaneous zone is integrated into vadose
flow conduits. This network of conduits then integrate or
converge to form the main lateral conduits which drain away from
Lemon Lane to the various other springs as shown by the tracer
test. This is shown conceptually in Figure 4. Because of the
greater degree of cross- and inter-connectivity in the
sub-cutaneous and vadose flow network, during high flows when
the system is backflooded, the tracers become dispersed
throughout this epikarstic zone. As the flood flows recede the
tracers are distributed radially to the main lateral conduits
which convey them to the various springr. This results in the
radial flow pattern as depicted in Figure 5.
However, it should be emphasized that the Quarry Spring
System (including Illinois Central Spring) is the major lateral
conduit draining the Lemon Lane Landfill, as is schematically
depicted in Figure 4. During a low flow tracer test conducted
-10-
in 1987 the Quarry System was the recipient of most of the flow,
with a minor component seeming to show up at Urban and Crestmont
springs. During the high flow test the Quarry system received
the earliest dye pulse and the largest amount of tracer mass
(i.e. the highest concentrations of tracer for the longest
period of time). Also, of the springs previously tested for
PCBs with the exception of one analysis at Stony East spring,
Quarry (and Illinois Central) had the only positive detection
for PCBs. It is the backflooding and backing-up of water in the
Quarry system which may be causing the distribution of the
tracer throughout the epikarst and consequently to so many of
these other springs.
-11-
FIGURES
-12-
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from Gunn (1985) ' A Conceptual Model for Conduit Flow Dominated KarstAquifers" Int'l Symposium on Karst Water Resources
PROJECTLemon Lane LandfillHigh Flow Tracer Test
(WJ WestinghouseN/ASCALE:
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Slaughter House Bypass 37 Cascade Br.PH Road Defeat Cr. West Stouts Cr. WestSnoddy A & B Defeat Cr. East Stouts Cr. EastHinkle t Kirby Road 111 Cen. e Allen St.Detmer A ' Sinking Creek Weimer RoadDetmer B Clear Cr. § HillsideRobertson 7th and AdamsPumping stationCrestmont17th StreetUrbanIllinois Central Sp.ICG-6ICG-3ICG-2ICG-1QuarryWN-1WS-2Stony WestStony East
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APPENDIX
Report on Analysis and Reporting Procedure for Bromide Tracer Test
A total of 739 samples have been analyzed for there bromide content osing
Suppressed Ion Chromatography (Dionex model 4500) and a Spectra Physics 4270
integrater.
Calibrations were performed using a multi-level (multi-standard) linear method.
For samples thought to have a low bromide concentration, 3 levels (0.1, 0.5 and 1.0 ppm)
with two injections per level was used for calibration. Samples with higher bromide
concentrations were analyzed using a 5-level calibration (0.1, 0.5, 1.0, 2.0 and 5.0 ppm),
with 2 injections at each level.
After calibration was completed, standards of known concentration were injected to
check for accuracy of the calibration. If the determined values were within 10 % of the
known concentration, calibration was assumed to be acceptable. Bromide standards were
also injected after every sixth sample during sample analysis to be sure calibration was
"holding". If, on any of these standards, the measured bromide value was more than 10%
different from its known concentration, re-calibration was performed.
Standards were prepared from a stock lOOOppm bromide solution. A 10 ppm
bromide standard was prepared first and was used to make the 0.1, 0.5, 1.0, 2.0 and 5.0
ppm standards. Standards were initially prepared on 5-9-89, but due to age of these
standards, a new set was prepared on 7-3-89.
The lowest standard used for calibration was 0.1 ppm in all cases. The integrater
program however, can extrapolate below this level, and bromide concentrations can be
reported at some value less than 0. Ippm. Hence, I have reported the value determined by
the integration program.
Bromide has a retention time of approximately 2.55 minutes on the Dionex 4ASA
column. Nitrate is the next anion eluted from the column, with a retention time ofapproximately 2.8 mi mites. If a sample contains substantial amounts of NO3~ , the nitrate
peak will interfere with the bromide peak, and it is very difficult for the integrater to
differentiate the two peaks. A visual examination of such a chromatogram reveals that there
is a very small quantity of bromide present in the sample. However, the integrater can not
accurately separate the NO3~ and Br peaks and often reports an unrealistically high value
for bromide. In such cases I have reported the bromide values as <0.10, because in every
case the Br peak was substantially smaller than that of the 0.1 ppm bromide standard.
A few samples had bromides concentrations greater than 5.0 ppm. In most cases
the concentration was determined using 1:2 dilutions to bring their measured bromide
values within calibration range. (MW-B4 was analyzed from a 1:40 dilution and MW-1D
was analyzed at a 1:2000 dilution). In the tables of data, any value with a superscript "d"
represents a value determined by an average of duplicate runs, if the values where within
10% of each other.
During the analysis of more than 700 samples,the exchange column did experience
some degradation, as the retention time of bromide dropped from 2.55 to 2.45 minutes.
This decrease in retention time posed no problem in the accurate determination of bromide
concentrations. Average area under peaks from injection of standards is shown in Table 1.
In all cases areas were within 10% of the mean peak area. Values vary in a random
fashion, indicating that there was no systematic shift in measured bromide concentrations
based on peak area variability.
WESTINGHOUSE HIGH FLOW TRACER TESTLEMON LANE
BACKGROUND BROMIDE (ppm)4/21/89
Site Concentration (ppm)
1 Cascade Branch 0.0952 Pumping Station 0.0973 17th Street 0.0984 Urban 0.0515 Crestmont 0.0766 37 Bypass 0.1147 Stouts Creek (West) 0.008 Stouts Creek (East) 0.009 Packing House Road 0.03610 . Packing House Culvert 0.04511 Slaughterhouse 0.04412 Snoddy B 0.02713 Snoddy A 0.04414 Detmer 0.0015 Robertson 0.05116 Defeat Creek (West) 0.0017 Defeat Creek (East) 0.0018 Kirby Road 0.0019 Sinking Creek 0.0020 Stony Spring (West) 0.0821 Stony Spring (East) 0.0022 Weimer Road 0.0023 Quarry Spring 0.0024 WN1 0.14325 I l l i iois Central (Allen Street) . . 0.10126 Clear Creek and Hillside 0 .14627 ICG 6 0.15428 ICG 3 >1029 ICG 2 0.92630 ICG 1 0.18231 Illinois Central 0.11632 Well 8S 0.07033 Hinkle
URBANTIME FLOH
7.89.611.514.114.818.731
36.742.449
55.171.395.6118.8141.9166.8262.5333.9501
669.7841
1004.91146.91363.9
SPC
480470506490490500521540578555570587601605609626595638740679697637518691
BR -
00.18000
0.040.090.090.10.10.10.10.10.110.110.110.10.120.070.670.30.090.060.08
QUARRY0 SPRING
18000040909010101010101101101101012070670300906080
TIHE
6.58.510.412.919.331.436.943
49.355.369.893.8118
140.1164.7267.8332.3500.7652.3840.31004.71147.51364.7
FLOW
129812981238147412981122987987936862642428353412198
. 428179229100553001424121
SPC
460450400406435454470458460487524545577565575499542633656615577382647
BR -
10.57.465. 844.252.451.180.971.041.041.030.710.721.231.441.50.430.740.680.850.92.5o.se2.82
1050746584425245118971041041037172123144150437468859025088282
CLEARCREEK ATHILL
1119.530.136
42.148.154.169.392.9117.3139.6164.2334.2500
651.9839.31004.11146.61363.5
565633637632634650630655679474630628643645565561601578563
0.070.090.30.130.130.110.120.140.130.140.140.150.130.160.212.960.151.450.18
ROBERTSON7090300130130110120140130140140150130-160 '21029601501450180
11.218.731.137
43.148.754.770.794.5118.2
141166.1334.5501.1668.8837.81005.71149.11365.8
365408417435380451448439467475487510500500562574507381528
0.040.040.060.050.050.050.040.10.050.10.080.070.060.080.10.150.120.070.14
40406050505040100501008070608010015012070140
HINKLE IC6-2
TINE FLOW SPC BR -(HOURS (6P«) (u5) (H6/L)AFTER 01
50 6.9 11.5 30090 8.9 9.80 10.8 8.20 13.3 8.2
ERR 19.5 1.00 30.6 0.6 33890 42.8 3.6ERR 54.5 1.090 69.7 1.090 93.6 1.0100 117.8 1.0100 139.9 1.0110 164.5 1.0ERR 332.8 1.0100 500.5 1.0,ERR 652.2 1.0ERR 839.7 1.0ERR 1004.4 1.0ERR 1146.9 9.8110 1363.9 1.050
ERR
TIME(HOURSfiFTER 0)
7.19.0
10.913.514.118.231.836.542.348.454.270.293.8
117.7263.3332.7500.6668.6837.3
1004.91149.31365.3
Tilt(HOURSftFTER 0)
7.19.1
10.813.319.730.542.754.469.693.5
117.7139.9164.5332.6500.3652.2839.8
1004.31146.81363.8
FLOW SPC(6PH) (uS/10)
_
----
28.5--
17.79.86.82.00.00.09.8--0.00.0---
ICB-3
FLOW(6PN)
6.46.44.84.8
11.51.51-5
1.51
1.11I
0.261.5I1
1.511
4238.935.936.3-
38.444.444.546.446.250,149.8--
54.1----
62.637.3-
SPC(uS)
1200----150--------------
BR -(M6/LI
0.050.090.000.00-0.000.09-0.090.090.100.100.11-0.10----0.110.05-
BR -(H6/LI
--------------------
TIHE FLOH SPC BR -(HOURS IGPN) (uSI (N6/UAFTER 0)
PH 8.5CULVERT 10.5
12.514.618.530.936.242.148.153.969.993.6117.5140.4165.5262.8332.4500.3668.3837.21004.81148.11365.1
35.135.135.120208.23.64.55.63.63.63.62.73.64.5--------
KIR8Y STONY EAST
TINE(HOURS
FLOW(GPN/io)
SPC(uS)
BR -(N6/U
AFTER 0)
M.821.930.737.343.549
55.271
94.811B.4141.3166.3333.5501.4669
838.21006
1149.31366.3
3803602802802752702702402101851501209690463112040090
345387378385392392380386422393431418520460475479431295459
0.03-
000
0.020.080.020.10.020.10.020.080.030.040.020.070.10.05
30ERR0002080201002010020803040207010050
TINE(HOURSAFTER 0)
13.820.331.236.743.348.954.?70.594.5118.7140.5164.9333.4501.7652.8838. S1005.81147.91365.2
FLOW(6PN)
130078533018818810075755040
* 20* 20--UNUNUN
1850-
SPC(uS)
432447497467508345524523540567544558549653624489559460609
BR -(H6/U
0.040.1-
0.040.040.030.040.040.050.070.060.04
00.050.070.090.070.050.06
40100ERR4040304040507060400507090705060
SINK1N6 CREEK STONY NEST
TINE FLON(HOURS (6PN)AFTER 0)
SPC(uS)
BR -(N6/L)
TINE FLON(HOURS (6PH1AFTER 0)
SPC(uS)
BR -(N6/L)
14.520. B30.837.443.649.255.371.294.9118.7141.4166.6333.7501.6669.3838.31006.21149.51366.5
770410340330295330295290290270215215225250215180205
> 2000270
285311356382393411431405432477425448424394419375385269373
0.10.050.060.060.060.050.060.050.060.090.070.060.10.090.160.180.090.060.25
1005060606030605060907060100901601809060230
1420.4
3136.643.249
54.970.394.3118.5140.4164.9333.3501.6652.7838.91005.61147.81365. 1
269288284294310503326344355391431431405491325597394287464
0.070.020.050.050.050.05-
0.010.010.020.020.030.020.060.10.050.070.040.09
702050505050
ERR!010202030206010050704090
HElttER ROAD HN-1
TINE(HOURSAFTER
13.517.531.336.943.549.255.170.894.6118.9140.6165.1333.5501.8652.8839.01005.81148.01365.3
FLOW(6PN/10)
0)_
-320445445353420440440325260-159205234620575089
SPC(uS)
326319340330327329325328350LOST362374415491406478395333460
BR -(N6/L1
0.020.010.010.010.010.020.020.010.110.040.020.010.030.100.070.330.080.050.06
2010101010202010
1104020103010070330805060
TIHE(HOURSAFTER 0)
11.920.130.836.442.948.654.670.094.0118.1140.3164.8333.6501.3652.5839.11005.31147.51364.8
FLOW(6PN)
28.546.635.128.522.720.020.015.48.23.62.71.0
-2.70.00.0W38.7-
SPC(uS/10)
62.665.465.668.263.871.564.471.123.175.975.180.976.778.6--77.963.6-
BR -IH6/L)
0.160.160.090.160.110.100.100.110.130.140.150.180.160.14--0.140.09-
16016090160110100100110130140150180160140ERRERR14090
ERR
ILLINOIS CENTRAL AT ALLEN KS-2
TINE(HOURSAFTER 0)
11.219.630.236
42.348.254.269.393.3117.4139.7164.3333.9500.2651.9839.21004.21146.71363.9
FLOH(GPU)
--220020001750160014501000620420300300245400160
< 100< 1004200125
SPCluS)
606601556558622355635690759823830835947100399510748245851005
BR -(KG/L)
5.491.180.8-0.63-0.70.520.440.7O.B0.810.46-0.450.411.140.491.6
54901180800ERR630ERR700520440700800BIO460ERR45041011404901600
TIHE(HOURSAFTER 0)
11.820
30.836.443
48.754.770.194.2118.2--333.8501.4652.6839.11005
1147.61364.9
FLDH(6Pfl>
50.825.59.83.61.5
< 1< 1< 1
0000
-< 1
00
< t113.5-
SPC(uS)
380398636396387620341310333347---441--463390-
BR -(H6/L)
0.30.30.330.30.50.70.220.20.210.21---0.31--0.250.28-
300300330300500700220200210210ERRERRERR310ERRERR250280ERR
CRESTHONT SLAUGHTER HOUSE
TIME(HOURSAFTER
7.69.311.313.915.018.930.936.542.748. B54.971.095.4118.7141.7166.7•>62.7333.8501.2669.0B40.81005.11146.31364.3
FLOW(BPNxlO)
0)
200.0255.0351.0317.0200.0200.0154.098.098.098.098.066.045.036.036.027.082.020.036.010.010.010.0134.010.0
SPC(uS/10)
2850
52.552.854.155.754.957.759
60.161.261.665.962
70. B70.264.676.880.778.980.77356
81.6
BR -(H6/L)
0.110.090.000.100.050.040.050.050.050.050.060.060.070.080.080.070.020.120.080.130.170.140.080.23
110900
100504050505050606070BO8070201208013017014080230
TIME(HOURSAFTER 01
6.48.510.512.414.518.431.936.242.048.153.869.893.6117.5140.4165.5232.6332.4500. i668.3837.21004.61148.01365.1
FLOW<6PH)
198.0179.0219.0198.087.3120.8113.575.670.255.355.342.528.525.520.09.828.59.89.83.64.515.4179.09.8
SPC(uS/IOJ
5459
57.7SB. 859.66163
66.467.467.768.670.368.370.873.777.267.8-75.481.583.78576
SB. 7B1.2
BR -(HG/LI
0.130.050.040.040.030.040.040.040.040.050.070.070.000.050.060.060.060.050.040.090.080.110.070.12
1305040403040404040507070050606060SO40908011070120
PACKING HOUSE ROAD SHODDY A t 8
TIRE(HOURSAFTER 0)
6.7B.610.613.214.61B.531.936.342.248.153.969.993.6117.5140.4165.5262.8332.4500.3668.3837.21004.81148.11365.1
FLQH(GPN)
152.0152.0219.0-
152.01B8.6136.0106.6100.093.487.375.635.12B.517.720.055.315.425.511.55.615.4179.09.8
SPC(uS/10)
6455.859.957.556.862.565.766.565.668
67.468.668.371.174.375.568.873.582.181.288
72.658. 482. B
BR -(H6/L)
0.070.020.030.020.030.030.040.050.040.110.040.050.050.050.060.060.040.060.070.080.070.100.080.12
70203020303040504011040SO50SO6060406070807010080120
TINE(HOURSAFTER 0!
7.08.710.813.314.018.331.736.442.348.354.170.193.8117.7140.6165.7263.1332.9500.7668.5837.31004.91148.31365.3
FLOW A(6PNI
15.422.722.7-9.89.817.711.535.155.365.031.74.53.61.55.69.84.53.63.65.68.265.03.6
FLOW B(6PW
171.0177.0465.0204.0158.0158.0226.3129.5226.3109.099.5208.441.422.98.311.833.714.59.41.5
< 1.08.3
250.04.1
SPC(uS/10)
4137.240.437
37.631.7
4141
39.739.442
40.247.450.751.253.246.854.657.960.558.554.436.857.9
BR -(HG/L)
0.020.040.090.030.020.020.030.020.020.020.020.030.020.100.050.040.040.050.070.090.060.090.060.09
20409030202030202020203020100504040SO709060906090
17 th
7th VADANS
TINE FLOW(HOURS (6P«)AFTER 0)
6.78.610.513.019.331.536.943.149.355.469.893.8117.9140.1164.6332.1500.71004.61147.41364.7
ICG-6
TINE FLOH(HOURS (6PH)AFTER 0)
11.819.730.436.142.348.454.369.593.4117.6139.8164.4263.0332.3500.3652.0840.11004.31146.81363.8
SPCUS)
450450S355626156756607036806897231500765799783775834785495844
SPC(uS)
440465472470502502514535603647721722602720799771819717439831
BR -(H6/L)
0.040.000.000.000.050.060.060.070.060.060.070.090.100.100.730.160.100.240.070.11
BR -(N6/L)
0.070.040.050.050.050.070.050.060.080.070.110.110.090.090.100.160.240.120.060.15
400005060607060607090too10073016010024070110
70405050507050608070110110909010016024012060ISO
TIHE FLOH(HOURS IGPtl)AFTER 0)
7.79.411.414.014.B18.830.936.642.548.955.071.295.5118.8141.8166.7262.6 - '333.9501.1669.71005.01146.31364.2
IC6-1
TINE FLON(HOURS (6PN)AFTER 0)
6.B8.810.713.119.430.736.342.848.554.569.793.7117.B140.0164.6332.9500.61004.51147.01364.0
SPC(uS)
770
740723630680716746740760761755776792792817839729850937817834712897
BR -(N6/L)
0.070.100.080.090.080.080.080.080.090.090.090.120.110.110.100.110.110.110.110.140.160.120.16
70100809080808080909090120110110100110110110110140160120160
SPC(uS)
BR -(H6/L)
560540538557563551539561555576555572588572556564616575498555
0.270.580.480.330.220.14-0.120.120.140.130.130.220.220.230.120.090.270.100.10
270580480330220140ERR12012014013013022022023012090270100100
CASCADE BRANCH STOUTS CREEK EAST
TIME(HOURSAFTER 0)
10.418.030.636.341.948.754.769.293.0116.5139.9165.0331.7667.7799.6834.31004.11147.21364.3
FLO*<6W
410520140240400265265180400100100100215100700180100165050
STOUTS CREEK
TINE FLON(HOURS (6PH/10)AFTER 0)
10.718.330.436.242.148.554.569.393.2117.2140.2165.2332.1499.9667.8836.810M.31147.51364.5
300180100906757
49.53723
13.51010101010101016023
SPC(uS)
5766146306506456646336046466676326676B3667727743689485645
NEST
SPC(uS>
377401416325425417438453455466468485504570542535502384510
BR -(N6/L)
0.040.040.050.050.050.060.060.060.070.080.070.080.090.430.090.100.130.150.14
BR -(J16/L)
0.170.040.020.030.030.030.030.040.030.040.040.040.050.050.070.030.080.070.08
404050SO50606060708070809043090100130150
• 140
170402030303030403040404050507030807080
T1HE FLOW(HOURS (GPN/10)AFTER 01
10.718.230.336.242.148.454.469.393.2117.2140.2165.2332.1499.8667.8836.81004.31147.51364.5
370600190
177.5162.514514513011095807733
107.517336653087
SPC(uS)
435447452460473457456469485475495505486566512552527397112
BR -(H6/L)
0.05-0.040.050.030.030.050.030.040.050.050.050.040.060.090.070.090.060.09
BYPASS 37
TIKE(HOURSAFTER 0)
11.018.532.136.142.348.354.369.793.4117.3140.3165.3332.3500.0668.0837.01004.51147.81364.8
FLON(6PN)
1709544587544444440321022364455321405
SPC(uS/101
65.368.272.172.859.472.474.277.381.478.886.587.483.483
91.294.183.762.890.5
BR -(NG/U
0.070.040.050.050.050.060.060.090.090.100.140.120.120.130.170.160.170.090.20
50ERR4050303050304050505040609070906090
70405050506060909010014012012013017016017090200
DEFEAT CREEK EAST DETNER A
TINE(HOURSAFTER 0)
11.318.930.937.243.348.954.970.894.7118.3141.21 to. 3333.3SOI. 3668.9838.01005.81149.31366.1
FLOW(6PH)
157512009501550830715715710400330255135180230* 50* 50115165060
DEFEAT CREEK
TIKE(HOURSAFTER 0)
11.318.830.937.243.348.954.870.894.7118.3141.2166.3333.3501.3668.9838.01005.81149.31366.1
FLOM<6PH)
_
------------------
SPC(uS)
365381385392405376366383395396417423439448501512441359464
NEST
SPC(uS)
376391383396406403410343417414441452445---465303-
BR -(N6/L)
0.030.06-0.030.030.020.030.030.040.030.030.030.030.040.050.030.040.040.05
BR -(N6/L)
0.030.020.030.020.000.000.080.030.050.030.050.03-0.03--0.040.05-
3060
30302030304030303030405030404050
TINE(HOURSAFTER 0)
11.619.131.436.742.848.554.470.494.2117.9140.8165.8333.1500.8668.7837.61005.31148.91365.7
TINE(HOURAFTER 0)
11.619.231.336.742.848.554.570.494.2117.9140.8165.8333.1500.8668.7B37.61005.31148.81365.7
FLOW(8PN)
.------------------
DETNER
FLOM(6PN)
113.565.028.5113.542.531.720.02.79.8
< 1< 1< 1----0.6
252.0-
SPC(uS)
449445463450475487463493487498517537537524585616518380568
B
SPC(uSl
428460456455484473500484508469517527431522--527426559
BR -(H6/L
0.080.080.110.050.080.070.050.080.080.080.090.09
00.090.140.120.130.070.15
BR -(H6/L
0.100.110.090.100.100.080.080.080.090.090.110.110.030.09--0.200.120.12
ILLINOIS CENTRAL SPRIN6
TIME FLOW(AFTER (6PH)HOUR 0)
6.38.310.312.819.131.236.842.949.171.596.0119.1142.2167.0333.5500.9669.4840.61004.81147.31364.5
SPC(uS)
3903903963i6417425422431454529510547547570574611625635557360641
BR -(H6/L)
8.706.704. IB2.121.351.401.021.221.250.671.171.951.622.221.100.741.4B1.223.691.604.00
8700670041802120135014001020122012506701170195016202220110074014801220369016004000
PUHPINS STATION
TIME FLOW
(HOURS (6PN)AFTER 0)
7.69.2
11.213.814.918.830.836.4
42.654.870.891.3 ; -
118.5141.6166.5333.8501.1669.8840.8
10051146.313M.3
SPC<uS>
600610603553573593631636665650679638628699725619760612368680601635
BR -(H6/L
0.070.340.090.060.060.060.070.070.060.070.080.080.090.090.090.070.070.090.030.160.090.11
Sargent Well
Date Time
5/29/89 12155/30/89 09455/31/89 08556/01/89 08256/02/89 08406/09/89 0815
Pelfree Well
Date Time
Well MW-6
5/29/89 11555/30/89 09405/31/89 09306/01/89 09256/02/89 10106/09/89 0840
Well MW-5
Date Time
Well MW-11"
Date Time
5/26/895/27/89
5/28/89
5/29/895/30/895/31/896/01/896/02/896/09/896/22/89
23440525191501000700131019031030105510100910094009081045
Br- in ppm
1.921.120.950.900.780.50
Br- in ppm
2.452.263.672.491.981.09
Br- in ppm
5/26/895/27/89
5/28/89
5/29/895/30/895/31/896/01/896/02/896/09/896/21/89
23300525190000450640130018491025104009550855093009001015
0.080.080.020.020.020.020.020.000.000.020.020.010.010.08
Br- in ppm
0.110.000.020.040.000.010.010.010.030.030.020.040.030.05
Date Time Br- in ppm
5/26/895/27/89
5/28/89
5/29/895/30/895/31/896/01/896/02/896/09/896/21/89
230605001855003506301225183910151025:09450850092508551420
0.000.000.000.000.000.000.000.030.000.060.020.030.030.08
Well MW-8d
Date Time
Well MW-8s
Date Time
5/26/895/27/89
5/28/89
5/29/895/30/895/31/896/01/896/02/896/09/896/21/89
22370445183000050600123518150955100009000840084508250830
Br- in ppra
5/26/895/27/89
5/28/89
5/29/895/30/896/01/896/02/896/09/896/21/89
1031043518300015060512401823100010050835085008301645
2.381.852.612.072.221.992.222.032.062.882.722.372.23
Br- in ppm
0.000.000.000.000.000.000.000.000.000.170.240.230.070.05
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