557 IL6of 1994-7 Q0tf( ,OUsU, T OSWEGO WETLAND MITIGATION SITE: FINAL HYDROGEOLOGIC CHARACTERIZATION REPORT (U.S. Route 34 at Waubansee Creek Oswego, Kendall County, Illinois) James J. Miner Christine S. Fucciolo Michael V. Miller Illinois State Geological Survey Lakes, Streams, and Wetlands Unit 615 East Peabody Drive Champaign, Illinois 61820-6964 Submitted under Contract No. AE89005 to Illinois Department of Transportation Bureau of Design and Environment, Wetlands Unit 2300 South Dirksen Parkway Springfield, Illinois 62764 October 21, 1994 Illinois State Geological Survey Open File Series 1994-7 •ssa? OSWEGO WETLAND MITIGATION SITE: FINAL HYDROGEOLOGIC CHARACTERIZATION REPORT (U.S. Route 34 at Waubansee Creek Oswego, Kendall County, Illinois) James J. Miner Christine S. Fucciolo Michael V. Miller Illinois State Geological Survey Lakes, Streams, and Wetlands Unit 615 East Peabody Drive Champaign, Illinois 61820-6964 Submitted under Contract No. AE89005 to Illinois Department of Transportation Bureau of Design and Environment, Wetlands Unit 2300 South Dirksen Parkway Springfield, Illinois 62764 October 21, 1994 Illinois State Geological Survey Open File Series 1994-7 Digitized by the Internet Archive in 2012 with funding from University of Illinois Urbana-Champaign http://archive.org/details/oswegowetlandmit19947mine CONTENTS INTRODUCTION 1 METHODS 2 GEOLOGY 3 Regional Setting 3 Site Characterization 5 Conclusions 7 HYDROLOGY 7 Regional Setting 7 Site Characterization 7 Conclusions 10 Monitoring 1 1 SUMMARY 11 ACKNOWLEDGMENTS 1 1 REFERENCES 12 APPENDIX A Geologic Cross Sections and Logs of Borings at Oswego Site 13 Parti Index of Geologic Symbols 13 Part 2 Geologic Cross Sections 14 Part 3 Geologic Logs of Borings 16 APPENDIX B Water-Level Elevations and Depths to Water Below Land Surface 28 APPENDIX C Well Construction Information 30 FIGURES 1 Study area and vicinity 1 2 Site map showing boring/well locations, stage-gauge locations, cross sections, proposed mitigation site, and existing wetland area 2 3 Geologic map of the bedrock surface showing bedrock units in northeastern Illinois 4 4 Portion of the map of the surficial geology of the Chicago region showing the stratigraphic units below the study area 5 5 Portion of a map from So/7 Survey of Kendall County, Illinois, showing soils in the study area 6 6 Hydrograph showing water-level elevations in wells and stage gauges in the study area during monitoring between January 1993 and March 1994 8 7 Chart showing depth to ground water, referenced to land surface, at each well site in the study area during monitoring between January 1993 and March 1994 8 8 Site map showing well locations and contours of the potentiometric surface within sand unit C (Henry Formation) on March 18, 1994 10 TABLES B1 Water-level elevations 28 B2 Depth to water in monitoring wells referenced to land surface 29 C1 Construction information for monitoring wells 30 INTRODUCTION This report was prepared by the Illinois State Geological Survey (ISGS) to provide the Illinois Department of Transportation (I DOT) with information regarding the hydrogeologic charac- terization and conditions during short-term monitoring in the potential wetland mitigation site described below. This report provides geologic and hydrologic data for the study area and describes planned long-term monitoring by ISGS. The Oswego site is located north of U.S. Route 34 at the easternmost bridge crossing Wau- bansee Creek on the east side of Oswego in Kendall County (T37N, R8E, Sec. 9, SE 1/4). The study area is outlined in figure 1 . The study area includes an existing wetland and the potential wetland mitigation site (fig. 2). IDOT requested that (1) the ISGS determine the suitability of the potential site for wetland mitigation; and (2) the existing wetland south of the mitigation site be included in this study in order that the hydrogeologic parameters of that wetland be determined and considered in designing the mitigation site. No geochemical characterization or monitoring was requested. ' \t'TX wmk* Ormvg" t*vr-Cb « 0 S WE G O 1 «*•* 0 1 1 mi I 1 0 I 2 km Figure 1 Study area (outlined) and vicinity, as shown on the Aurora South 7.5-minute topographic map (USGS 1954). Contour interval is 10 ft (3 m). Figure 2 Site map showing boring/well and stage gauge locations, cross sec- tions, proposed mitigation site, and existing wetland area. Topographic contours are in meters referenced to National Geodetic Vertical Datum of 1929 (NGVD, 1929); contour interval is 3 m (10 ft). In the summer of 1993, two excavations were made in the mitigation site adjacent to Waubansee Creek. Surface- and ground-water levels in the study area will be monitored through September 1998 or until monitoring is no longer required by IDOT. A final monitoring report will be prepared by ISGS at that time. METHODS A series of seven borings was made to determine the geology of the study area (fig. 2). Borings 1 and 2 were made by driving an aluminum pipe 76 mm (3 in.) in diameter into the ground to depth, then extracting it to obtain a relatively undisturbed sample. Borings 3, 4, and 7 were made using a Mobile B-30S drilling rig with an 82 mm (3.25 in.) inner diameter hollow-stem auger. Continuous sampling was performed while drilling these borings. Borings 5 and 6 were made using a 76-mm (3-in.) diameter hand auger. Monitoring wells were installed in each geologic boring to determine the hydrology of the study area. Stage gauges were installed in Waubansee Creek at points A and B (fig. 2) to monitor creek levels. Monitoring wells were constructed of 2.54-cm (1 -in.) diameter Schedule 40 PVC pipe with 0.76-m (2.5-ft) slotted well screens; slot size was 0.25 mm (0.01 in.). Wells installed in borings made with the Mobile drilling rig were constructed with a filter pack of 0.25-0.5 mm (0.010-0.020 in.) diameter quartz sand placed in the annulus from the base of the well screen to approximately 0.3 m (1 ft) above the top of the well screen. A seal of bentonite was placed above the filter pack. The borings were backfilled with differing amounts of bentonite and cuttings. Appendix C reports all well construction measurements. Well screens installed in hand-augered borings were partially or fully driven to depth into undisturbed materials below the base of the boring. Any well screen not fully driven below the base of the boring was packed with sand, as described above. Wells were sealed with bentonite to the land surface. Protective covers were placed over each well. Covers for borings made with the Mobile drilling rig were set in approximately 0.3 m (1 ft) of concrete. Elevations of wells and stage-measuring points were determined by leveling to third-order accuracy from benchmarks provided by IDOT. A Sokkia B-1 automatic level and fiberglass extending rods were used. GEOLOGY Regional Setting Bedrock The uppermost bedrock unit at the Oswego site consists of shaly and cherty dolomites of the Alexandrian Series of the Silurian System (fig. 3) overlying shales and limestones of the Ordovician System (Willman 1971). The bedrock surface in this area is generally horizontal with bedrock units dipping approximately 2° to the east-northeast (Willman 1971). Quaternary Sediments Quaternary sediments increase in thickness from west to east across the study area (Piskin and Bergstrom 1975, and ISGS well records on file). Bedrock crops out adjacent to the Fox River approximately 1 .5 km (1 mi) to the west of the site. Sediment thickness increases to approximately 15 m (50 ft) below the site. Within the Minooka Moraine (fig. 3), 3 km (2 mi) east of the study area, sediments increase to greater than 30 m (100 ft) in thickness. Well logs from the region (ISGS records on file) indicate that sediments consist of approxi- mately 1.5-3 m (5-10 ft) of silty clay overlying 6-9 m (20-30 ft) of sand and gravel. Other minor sedimentary units are occasionally present below these beds. The silty clay deposited at the surface is classified as Cahokia Alluvium adjacent to Wau- bansee Creek (Berg and Kempton 1988) but may include Richland Loess away from Wau- bansee Creek (Curry et al. 1988). The underlying sand and gravel is classified as part of the Batavia Member of the Henry Formation (fig. 4), which was deposited in glacial outwash plains adjacent to moraines (Willman 1971). Glacial till of the Wedron Formation is present at the surface approximately 3 km (2 mi) eastward in the Minooka Moraine (Berg and Kempton 1988). Soils Figure 5 shows the soils located in the study area (U.S. Department of Agriculture 1978). A body of Sawmill silty clay loam soil, which is listed as hydric by the Soil Conservation Service (USDA 1991, rev. January 31, 1992), exists along the banks of the creek and within the present wetland south of the mitigation site. Soils in the mitigation area and in the remainder of the study area are not listed as hydric. Figure 3 Geologic map of the bedrock surface showing bedrock units in northeastern Illinois (from Willman 1971). Star indicates location of the study area. Figure 4 Portion of the map of the surficial geology of the Chicago region showing the stratigraphic units below the study area (from Willman 1971). Map units: hb = Batavia Member, Henry Formation; hm = Mackinaw Member, Batavia Formation; mi = Minooka Moraine, Yorkville Till Member, Wedron Formation; ms = Marseilles Moraine, Yorkville Till Member; mhg = Marseilles-Huntley Ground Moraine, Yorkville Till Member; S = Silurian bedrock. Arrow indicates study area. Topography The regional slope over the study area is westward approximately 3^ m/km (16-21 ft/mi) (fig. 1). Regional drainage is westward toward the Fox River. Site drainage is west and north toward Waubansee Creek, which in turn flows west-southwest toward the Fox River. Total relief in the study area is approximately 5 m (16 ft). Waubansee Creek is incised between 1.5-3 m (5-10 ft) below the adjacent land surface. Creek banks are steep and actively eroding in places. Site Characterization Data from the geologic borings were used to prepare two cross sections of the geology of the study area (Appendix A). Locations of the cross sections are shown in figure 2. Logs of geologic borings indicate that the uppermost unit of sediments across most of the study area Figure 5 Portion of a map from So/7 Survey of Kendall County, Illinois, showing soils in the study area (from USDA 1978). Soil types: 107 = Sawmill silty clay loam; 149 = Brenton silt loam; 325A/B = Dresden silt loam; 327C2 = Fox silt loam; 369A = Waupecan silt loam. Study area is stippled. is a body of sandy and clayey silt (labeled silt unit A), which probably contains both Richland Loess and Cahokia Alluvium (Berg and Kempton 1 988, Curry et al. 1 988). As shown in cross section A-A' (Appendix A), these sediments have been eroded in the floodplain of Wauban- see Creek. This unit is approximately 2.6 m (8.5 ft) thick near the east bank of the creek and thins to approximately 1 .5 m (5 ft) thick toward the eastern edge of the study area. This unit and underlying beds dip toward the northwest at approximately 1.2-3.0 m/km (6-16 ft/mi). A layer of peat (labeled peat unit B) occurs at the surface within the present wetland area in the floodplain of Waubansee Creek (fig. 2). The peat is classified as part of the Grayslake Peat (Willman 1971). This unit is approximately 0.76 m (2.5 ft) thick, including an underlying 0.46 m (1 .5 ft) thick layer of interbedded sand and peat. This unit occurs throughout the wetland area and truncates laterally against the creek to the west and the edge of the floodplain to the east, as shown in cross section A-A'. Below silt unit A and peat unit B lies an interval of bedded sand and gravel (labeled sand unit C) correlated with the Batavia Member of the Henry Formation (Berg and Kempton 1988). This unit is approximately 7.0 m (23 ft) thick on the east side of the study area and thins to approximately 3.7 m (12 ft) thick near Waubansee Creek. Individual beds of sand and sandy gravel are up to approximately 1 m thick. Some silt and silty sand beds are pres- ent. Sands are medium to coarse and yellow to red. Gravel up to 50 mm (2 in.) in diameter is present. Below sand unit C lies a unit composed of silt loam and sandy loam diamicton interbedded with sand and gravel (labeled diamicton unit D). Diamicton is a term used to describe all very poorly sorted sediment, such as glacial tills and mud flows, without implying an origin of the sediment (Eyles 1983, p. 13). The thickness of each bed ranges from 0.1-0.5 m (0.3-1.6 ft). The base of this unit was not reached in borings made for this study; however, in a boring adjacent to the west side of the study area across Waubansee Creek (Curry et al. 1 988), this unit was approximately 4.0 m (13 ft) thick. As much as 2.0 m (6.5 ft) of this unit was pene- trated in borings made for this study. This unit is classified as Maiden Till Member of the Wedron Formation (Curry et al. 1988). Conclusions During the late Wisconsinan Stage, diamicton unit D (Maiden Till Member of the Wedron For- mation) was deposited across the study area. The origin of this unit is unknown, but it may have been deposited as a glacial till. Another possibility is that the diamicton may have been formed by debris flows and other mass movements from the Minooka Moraine during depo- sition at the front of the glacier. Afterward, sand unit C (Batavia Member of the Henry For- mation) was deposited above the diamicton as part of a sheet of outwash issuing from the Wisconsin glacier at the Minooka Moraine. The next unit to be deposited was silt unit A, which contains loess deposited across the site and alluvium deposited within and adjacent to Waubansee Creek. During this event, sand unit C was thinned by Waubansee Creek. Later, erosion exposed sand unit C in the floodplain of Waubansee Creek, providing a substrate for the deposition of peat unit B (Grayslake Peat) in the area of the present wetland. HYDROLOGY Regional Setting Water well records in the ISGS files indicate that water in private wells in the vicinity is obtained from various bedrock aquifers. No records are on file for wells obtaining water from Quaternary sediments. Waubansee Creek drains southwestward toward the Fox River, which is approximately 12 m (40 ft) lower in elevation. Because the Fox River has eroded to bedrock, it is probable that regional ground-water flow in Quaternary sediments of the study area is toward the river. Site Characterization Ground Water Monitoring wells were installed in all geologic borings to identify the local ground-water flow system and measure the levels of any sources of ground water that sustain the present wet- land and those that have the potential to sustain wetlands in the mitigation area. Monitoring wells and stage elevations were measured monthly during the study period. Because sand unit C is a shallow aquifer that underlies the entire study area, monitoring wells were installed at various depths and locations within sand unit C with the exception of boring 3. Figure 6 is a hydrograph showing ground-water measurements in each well and stage of Waubansee Creek from the time of installation to March 18, 1994. Figure 7 shows the depth to ground-water levels below land surface at each well. All well and stage readings are summarized in Appendix B. 199 196 o CnJ O o 198 - •*-i -a 0) k. (1) *-■ CO -o- Jan 93 Mar 93 May 93 Jul 93 Sep 93 Nov 93 Jan 94 Mar 94 May 94 - well 1 - well 2 - well 3 upper - well 3 lower ~ well 4 - well 5 - well 6 - well 7 upper - well 7 lower - gauge A - gauge B Figure 6 Hydrograph showing water-level elevations in wells and stage gauges in the study area during monitoring between January 1993 and March 1994. Jan 93 Mar 93 May 93 Jul 93 Sep 93 Nov 93 Jan 94 Mar 94 May 94 + 1.00 4.00 -D- -O- well 1 well 2 well 3 upper well 3 lower well 4 well 5 well 6 well 7 upper well 7 lower Figure 7 Chart showing depth to ground water, referenced to land surface, at each well site in the study area during monitoring between January 1 993 and March 1 994. Plus sign indicates water above land surface. These hydrographs can be used to infer general trends regarding the hydrology of the site. However, monthly readings do not record transient events and may attenuate the actual vari- ations in levels. Water levels in the study area during the monitoring period were highest in the spring when precipitation is generally high and evapotranspiration generally low (Hen- sel 1992). Water levels decreased during the summer when evapotranspiration generally increases and precipitation decreases. Changes in water levels also vary between wells. Irregular and rapid changes in level occur in relatively shallow wells (e.g. wells 1 and 2), as compared with deeper wells (e.g. well 3). During November 1 993, wells 1 , 2, 4, and 5 had sharp rises in water levels to the extent that ground-water flow reversed toward well 3. During this time, well 3 showed only a gradual rise in water level, which lasted several months longer than the higher water levels in the other wells. This may indicate that precipitation and seasonal changes in evapotranspiration strongly affect shallow wells, whereas longer term or regional conditions are more likely to affect deeper wells. Boring 7 contains wells screened in shallower and deeper portions of sand unit C. The bases of the well screens are at depths of 1 .52 m (4.99 ft) and 6.22 m (24.41 ft). Readings of water levels in well 7 on March 18, 1994, show a moderate upward gradient, indicating that ground water may have been discharging in this area at that time. Boring 3 contains well screens in sand unit C at a depth of 5.66 m (18.57 ft) and in sand beds within diamicton unit D at a depth of 8.71 m (28.58 ft). The difference in readings between these wells is negligible, indicating no significant vertical ground-water gradient between these two units at this location. Ground-water levels measured on March 18, 1994, are shown on the cross sections in Appendix A, Part 2. These levels show that sand unit C is artesian at boring 4 adjacent to Waubansee Creek, but not fully saturated in the remainder of the study area. Water levels indicate that ground-water recharge occurs from the east. Ground-water discharge to the sur- face occurs only in those areas adjacent to Waubansee Creek where erosion has thinned or removed silt unit A. This discharge was observed on April 20, 1994, when ground-water seeps were noted along the eastern edge of the south portion of the newly excavated miti- gation area. Additionally, ground-water discharge occurs in the present wetland area, as evidenced by often-observed seeps and standing water at the eastern edge of the floodplain, approximately 1-1 .5 m (3.3-4.9 ft) above the water levels measured in the creek. Additional monitoring wells will be installed to better characterize potential ground-water discharge in the mitigation area. Water levels in figure 8 show the potentiometric surface in sand unit C, as shown by readings collected on March 18, 1994. Contours of the potentiometric surface indicate that ground- water flow is in general toward Waubansee Creek. However, the reversal in flow shown by water levels recorded from November 1993 through February 1994 (fig. 7) indicates that the ground-water system in the study area may fluctuate, given appropriate conditions, and local ground-water recharge may occur adjacent to Waubansee Creek. Surface water Waubansee Creek was also examined for effects on the present wetland and as a potential source of water for the proposed mitigation area. Measurement of the water level in the creek began at stage gauge A on the U.S. Route 34 bridge in June 1993 (fig. 6). A second site, stage gauge B, was established in the spring of 1994. Observations regarding this source follow. / .'*' / gauge B .' 7 7^ ■ / '.6 / q \ % \ N ^ is 4 0 1 600 ft 1 jf gauge A 1 0 200 m >^ Figure 8 Site map showing well locations and contours of the potentiometric surface within sand unit C (Henry Formation). Water levels were measured on March 18, 1 994. Contour interval is 0.5 m. Arrows show estimated ground-water flow directions. Water levels in the creek have been relatively constant from July 1993 through March 1994, with the exception of June 1993, a period of heavy rainfall. Local residents stated that the creek has not flooded recently in an amount sufficient to overtop the banks. Additionally, ground-water levels in sand unit C flow toward and are above the level of Waubansee Creek. These data indicate that the creek is supplied by ground-water discharge from sand unit C. Conclusions Ground water recharges to sand unit C east of the study area and flows toward Waubansee Creek. Ground-water discharge occurs along and into Waubansee Creek where silt unit A has been eroded. Water levels in Waubansee Creek have been high enough to saturate a portion of the present wetland only in June 1993, a period of very high precipitation. Since that time, water levels in the creek have been below the base of the peat (upper portion of peat unit B) despite the saturated conditions frequently observed within the wetland adjacent to the creek. Therefore, Waubansee Creek is not the primary source of water sustaining the present wetland area. The stable water levels in Waubansee Creek reflect a significant ground-water input that would provide a constant source for base flow. It should be expected that higher water levels in the creek will be transient, relating to increased precipitation. 10 The present wetland is primarily sustained by ground-water discharge from sand unit C. This discharge is occurring within the present wetland along Waubansee Creek and along the southeastern portion of the newly excavated mitigation area where erosion or removal of silt unit A has occurred. Monitoring The ISGS will monitor this site to determine the water-level conditions after construction and during establishment of a wetland. Surface- and ground-water levels are currently being monitored monthly. Additional monitoring wells will be installed to better characterize potential ground-water discharge in the mitigation area. Monitoring will continue through Septem- ber 1998 or until no longer required by IDOT, after which a final monitoring report will be issued. SUMMARY Hydrogeologic characterization of the Oswego site has been completed and long-term moni- toring is in progress. Results of this continuing monitoring will be submitted to IDOT as required, with conclusions drawn, if applicable. A final monitoring report, containing all moni- toring results, will be issued by the ISGS after completion of scheduled monitoring in Septem- ber 1998, or as required by IDOT. Ground-water discharge into the mitigation area will be characterized during long-term monitoring. Bedrock in the study area is covered by approximately 15 m (50 ft) of sediments. These sedi- ments were not fully penetrated in borings made for this study. Seven borings indicate that the sediments covering this site consist of diamicton bedded with sand and gravel of the Wedron Formation (diamicton unit D) covered by approximately 6 m (20 ft) of sand and gravel of the Henry Formation (sand unit C). These sediments are capped by 0.9-2.4 m (3-8 ft) of silt and clay of the Cahokia Alluvium and Richland Loess (silt unit A). Waubansee Creek has eroded into the Henry Formation deposits in its floodplain, where a thin layer of Grayslake Peat (peat unit B) is present within the existing wetland area. Monitoring wells were installed in sand unit C and diamicton unit D to measure ground-water levels and to determine the direction of ground-water flow. Results indicate that sand unit C is not saturated in the eastern part of the study area, but is artesian in the western portion along Waubansee Creek. Water levels indicate that ground water flows from east of the study area toward Waubansee Creek. Ground-water discharge occurs along the banks of Wau- bansee Creek where erosion into sand unit C has occurred. The water level in Waubansee Creek is relatively constant, indicating a ground-water source. Local residents stated that Waubansee Creek does not overtop its banks during floods. The existing wetland in the study area is primarily supported by the discharge of ground water along the east bank of Waubansee Creek. Water levels in the creek during the moni- toring period have been insufficient to flood more than a minor portion of the wetland area and have generally remained below the base of the peat within the wetland. ACKNOWLEDGMENTS This study was supported by the Illinois Department of Transportation under contract number AE89005. Additional funding was provided by the Illinois State Geological Survey. 11 REFERENCES Berg, R.C., and J. P. Kempton, 1988, Stack Unit Mapping of Geologic Materials in Illinois to a Depth of 15 Meters: Illinois State Geological Survey Circular 542, Champaign, 23 p. Curry, B.B., A.M. Graese, M.J. Hasek, R.C. Vaiden, R.A. Bauer, D.A. Schumacher, K.A. Norton, and W.G. Dixon, Jr., 1988, Geological-Geotechnical Studies for Siting the Superconducting Super Collider in Illinois: Results of the 1986 Test Drilling Program, Illinois State Geological Survey, Environmental Geology Notes 122, Champaign, 108 p. Eyles, Nicholas (ed.), 1983, Glacial Geology: Pergamon Press, Oxford, England, 409 p. Hensel, Bruce, 1992, Natural Recharge of Groundwater in Illinois: Illinois State Geological Survey Environmental Geology 143, Champaign, 33 p. Piskin, Kemal, and R.E. Bergstrom, 1975, Glacial Drift in Illinois: Thickness and Character: Illinois State Geological Survey, Circular 490, Champaign, 35 p. U.S. Department of Agriculture, Soil Conservation Service, 1978, Soil Survey of Kendall County, Illinois, Washington, D.C., 77 p. U.S. Department of Agriculture, Soil Conservation Service, 1991 , Hydric soils of Illinois (rev. January 31 , 1 992), in Hydric Soils of the United States, Miscellaneous Publication 1 491 , Washington, D. C. U.S. Geological Survey, 1954 (photorevised 1980), Aurora South Quadrangle, Illinois, 7.5- Minute Series (Topographic): U.S. Department of the Interior, Geological Survey, Res- ton, Virginia, map scale 1:24,000. Willman, H.B., 1 971 , Summary of the Geology of the Chicago Area: Illinois State Geological Survey, Circular 460, Champaign, 77 p. 12 APPENDIX A Geologic Cross Sections and Logs of Borings at Oswego Site Part 1 Index of Geologic Symbols Gravel (includes boulde pebbles, and gr< Sandy gravel i ■'. •°" ' '. ■'. ■"■ • '. ■ Sand and gravel Sand ■ - - - Silty sand T.-..-T..T. -..-.. - Silty clay sand : lit. : ur: : . Clayey sand — — — Sandy silt Silt ■ - Clayey silt Silty clay - Clay A A ' A A A A t A A A A A A A A A A A A t A A A A A A A A A A A A i A A A A A A •At 1i iU ik iU Diamicton Peat ! ) I AU\ A> Black organic material Depth of soil development Roots No recovery 13 APPENDIX A continued Part 2 Geologic Cross Sections CROSS SECTION A-A' 202 201 200 199 198 197 196 195 194 193 192 191 190 189 188 CM Q > O Z ■o .2 in Waubansee Creek gauge A A' upper lower range in water level elevations maximum I elevation on 03/18/94 minimum __-- — -"""TjnitA :-:-:-:- Cahokia Alluvium/ Richland Loess ^^-^ (clayey siltt^-""'^ jGC Unite Henry Formation Batavia Member (sand and gravel) II 1 ■:•:■:■;■: ■:■ UnitD Wedron Formation Maiden Till Member L A A^t^ (diamicton) horizontal scale 300 ft •■ D screened interval 0 100 m vertical exaggeration 25x 14 APPENDIX A Part 2 continued Geologic Cross Sections m o ill n x CU > o; I ~ o _ o> "D-D •= ra m .5 E « E ■D co « a a) c ij rS co w li O) c CO m ■§£ ga6ne6 IliPfl jiijj,, i ;■;;■; ri eg o CM o CM o o CM 00 co CD o> co CD o co oo ao oo (6361. 'QAON oi psousjspj uu) uoiJBAaig APPENDIX A continued Part 3 Geologic Logs of Borings OSWEGO #1 Location SE SW SE, Sec. 9, T37N, R8E, Aurora South, Illinois Date 01/28/93 Field Crew Christine Fucciolo, Jim Miner Weather Conditions 0° F Comments Core collected by hammering an aluminum pipe 76 mm (3 in.) in diameter to depth. Well Information One well installed; construction information in Appendix C. Meters Feet 0_0 1 _ End l_5 Depth Unit Descriptions 0.00 - 0.35 m Black organic material; (N 2.5/); noncalcareous; visible root (0.00- 1.15 ft) material constitutes about 50%; silty texture with some fine sand; structureless; soft. 0.35- 0.67 m Bedded sand and peat Peat layers are 1-61 mm (1.15 - 2.20 ft) (0.04-2.40 in.) thick; no regularity in thickness; black (N 2.5/); spongy texture; noncalcareous; visible organic fragments comprise about 30%; moderately stiff. Sand layers vary in thickness from one layer of granules to 30 mm (1.18 in.); gray (10YR6/1); poorly sorted with grains ranging in size from granules to fine sand; poorly rounded. 0.67- 0.81 m Sand and gravel; gray (10YR 6/1); approximately 5% is silt; (2.20- 2.65 ft) poorly sorted; about 50% is gravel; pebbles up to 10 mm (0.39 in.) in diameter are rounded and consist of shale, dolomite, chert and granitics; densely packed; little pore space between pebbles due to sand and silt. 16 APPENDIX A Part 3 continued Geologic Logs of Borings OSWEGO #2 Location NE SW SE, Sec. 9, T37N, R8E, Aurora South, IL Date 01/29/93 Field Crew Christine Fucciolo, Jim Miner Weather Conditions 0° F Comments Core collected by hammering an aluminum pipe 76 mm (3 in.) in diameter to depth. Well Information One well installed; construction information in Appendix C. Depth Unit Descriptions 0.00- 0.18 m Black organic material; (N 2.5/); noncalcareous; soft; silty; (0.00 - 0.60 ft) crumb structure; visible stems, roots, twigs and leaves constitute 50%. Gradual contact over 0.03 m (0.10 ft) to: 0.18- 0.47 m Black peat; (N 2.5/); silty; noncalcareous; visible organic (0.60 - 1 .55 ft) fragments comprise about 30%; moderately stiff, especially near base where it is also spongy. Sharp lower contact to: 0.47 - 0.69 m Bedded sand and peat Peat layers spongy; dark gray (1 .55 - 2.25 ft) (2.5Y 4/1); about 40% is visible fragments of stems and roots; noncalcareous; layers up to 15 mm (0.60 in.) thick; some layers are mixed with sand. Sand layers poorly sorted with grains ranging in size from granules to fine sand and in thickness from one granule to 8 mm (0.30 in.) thick; poorly rounded; grains consist of quartz, rock fragments and feldspars. Gradual contact over 25 mm (1 in.) to: 0.69- 0.88 m Sand and gravel; light gray (5Y7/1); approximately 50% is (2.25 - 2.90 ft) granules and gravel, about 50% is fine to coarse sand; poorly sorted; tightly packed; pebbles up to 10 mm (0.39 in.) in diameter are rounded and consist of shale, dolomite, chert and granitics; no obvious bedding or structure. 17 APPENDIX A continued Part 3 Geologic Logs of Borings OSWEGO #3 Location Date Field Crew Weather Conditions Comments Well Information Meters Feet <) 0 1 _ 2_ 4_ _15 6_ 7 _. 10. 11 J .10 .20 _25 _30 &^ O Q "D C CD c o (0 > LU 1 J3 B iL (0 m x Q Z HI Q. Ol < m a) a 3 CD a 4 * ♦ * * * ♦ • « * * * * CO CD CM CO CD < CD -z. Well 7 upper * * * * * * * * • * * * 00 CO 1^ CD 00 CD 5 i^ CD CO * * * CO cd CD CO ■ O E CD T3 O E CD T3 CD > O E CD O E CD -o CD > O E CD o E CD CD > O E CD CD > o E CD o "O CD O C 0) ID k_ 05 C g CO > CD CD * * •K CO co 1^ CD C\l CD CO CO r-' CD o CD O CD CO CD CD CVJ 1^ CD in CO CD in CO CD CD C CD N O C CD N o <* "53 * * CO CO a> CM CD CO CD CD CD oo CO CD in CD CO CD in 00 CO CD in CD CO CD o CD CD CD CO CO CO CD 00 CO CO CD CM CD in o CD > _CD 0) as CO U = 1 * * CVJ CO CD O ■"3- 00 CT> CO CM od CD CD CO CD CD CD CO CD in CD CO CVJ CD 00 CVJ CD CVI CO CD CO CD CO CO h-' CD 5 CO 1- Well 3 upper * * CO CO cd CD 00 CO 00 CD CO CO CD CD in CO CD in CM CD CO CD 00 CD cvj CD CD CM t^ CD CO CO 1^ CD O i^ CD CD CD * CD CO CD CO CM 1^ CD CM in CD in CO CD CM CD CD 00 CD CD CD oo CO CD CD CO CM CD O CO 1^ CD in cvj CD c cm CO o CO CD o in o CO CD CD o CD o CO CD in cvj CO o CO CD CM CVJ O CO CD CM CO O CO CD evj CVJ CD O CO CD f^ CVJ O CO CD in CO CD CO cvi CD CO o C5 CD O CM o CD CO o CD CO CO o 1 1 CO Q) c = .5 w — CD CD o > o > O > O > O > o > O > o £ E E E E E E E 0 CD CD CD CD CD 0 0 T3 c _CO O) CO ,— ■- 0 N 0 Nl "D £ O o CD *^ ■*■■ CJ c CD i_ CD o o CO ■* CM Is- Is- CO T— CO CO o CD t CM CO id CO '— o ■»— o T— T— 1— OS q CD "53 * ^ c\i f- T- *- CM CM CM CM CM cm' CM ■^ T^ _w "CD 5 O) Is- O) co CO CO O) LO CO CD o Is- CM CO c CO i— o o CM Is- 1— CM CO CO CM CM 1— CO oo o "E "53 5 i O * 9 CM CM CM CM CO CO CO CO CO CO CO CM CM o E c CD o> CD O CM CM T- en CO 00 " in CO OS "tf CO T- CM o CM o T— CM LO ID CO CM T— CM c OJ CO Q. CD "53 * d d d + d d d d d d d d 0 N d d Q £ o CM CD CD CO CM CO r- CM CO CO CM ^r ID CO CM 00 CO Is- T~ O o CM T_ o rr ID tj- ■>a- t— CM C\J c o T— "53 d d d O + d d d d d d d d 0 N o d d 1- «S CO CO CO CO CO CO CO CO CO CO CO "* ■* ■* •sf a> en 0s en CD CD en en en en en en 5s cn 35 CM o o5 LO CM r^ CM i^ ID CO CO o5 ■^r oo CM ^— T— o CM CM CM CM CM ^- ^ T— o r- ^ co m CD CD r- oo o5 O i — CM ^ CM CO co o o o O o o o o o o o o c o 0 0 CD O m o 0 3 CO CO in "D r c aj 0
  • . > ^^ o O D 2 < 29 c o ■^ CO E a c c o ■o 3 % c o o © O >< o z UJ Q. a. < N u ■«a- ** CO o co CM CM O CD CD CO CO CD CD CM CD CM °8 IB "o — i Q. CD CO CM r- r- CO in O ■* ■ 05 CO C\j d d 00 i-^ d d d yl r^ CM c\i 00 d ,-J 5 3 CD cd QJ co .y X O DC r- i- in ■>*■ CO CD CM CM o CD CD CO CO CD CD CM CO CM cT 0 C\J CO CO CO r-- CO CM o <* ^* co CO in m CO •^■ CM "53 S OS CO cb d d 00 CO d d d ,-J ,_: CM CM CO in d c 0 £ o CD CD X (O 00 CO in CD CO -* Is- o •, o "* CO in i-- •f r- < < < < o CD oi ■<^ o Is- c a> o d CO* d d CM CM Z Z 2 2 d d d CM CM CM 0 £ o CM CD I in o ^ CO CO O in o O CD in cT c ■* *■ CO CM r- ,— in < < < < o CD S f"m f- in 0) O) CO CO T— d CM CM z 2 2 2 d d d CM T— CM 0 , £ CD CD 0 co o xo CD © CO H T" in ■* CD ,_ CO ,_ in o in in in CD in o3 jg — 03 ••"" r- CO r- CO CD < < < < o ■r" t_ CD T_ CD a> K h- T— d d d d •z. 2 2 2 d d d d d d C >% £ CD CD © co xo * * * * E "© c ^ If o o o o « Q. o , , "o "co > "© "e * o « * E~ "2 o 41 * £ O o E9, C/) "E" o «S E^ *o H CD J^, o H m J^ o "55 "55 > 0 E o Q. O 1- LU © o co 03 03 C CL "53 "55 CD "co CD O o m "55 0 "55 0 Q. O o m > 0 E "o 03 g c © c CD CO CO ^ ^^ CO CO ^ ^ c LL t: co C CD _l Q. 3 T3 CD 0 "c o co 0_ o co 0. 0 'E 0 "E O co CL o co D. T3 0 C T3 0 C T3 0 C 03 > CO T3 C 2 o a> © Q. E O C o c T3 C T3 C o c o T3 C T3 C 0 0 0 0 © © CC o o co CD CD 0 co co 0 0 CO co o o o LU _l t- CO CO CO D CO CO CO CO m m CO CO CO CO CO 0 C3 m CD CM 3 03 CD CD "n -SJ T— c ni ui > ffl CO f 1 > CO n u ** 2 0 n LL Q. O c F F ca CO C3 ffl c c 2 D 30