Geologic Atlas of Carlton County, Minnesota §¦35 §¦35 §¦35
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STATE OF MINNESOTA Prepared and published with the support of the COUNTY ATLAS SERIES DEPARTMENT OF NATURAL RESOURCES MINNESOTA ENVIRONMENT AND NATURAL RESOURCES TRUST FUND and the CLEAN WATER, LAND, AND LEGACY AMENDMENT ATLAS C-19, PART B, PLATE 7 OF 10 DIVISION OF ECOLOGICAL AND WATER RESOURCES Hydrogeology of the Surficial Aquifer R. 19 W. HYDROGEOLOGY OF THE INTRODUCTION R. 18 W. SURFICIAL AQUIFER This atlas is designed for units of government and citizens to use in planning for land use, water supply, St. Loui s and pollution prevention. The data and maps in this atlas show the distribution and physical characteristics of T. 51 N. Brookston the most important aquifers in the study area. They also describe the groundwater flow patterns, aquifer 36 31 35 By 34 relationships, groundwater chemistry, and sensitivity to pollution of the surficial and buried aquifers. The study ¤2 area consists of Carlton County and the portion of the Fond du Lac Band of Lake Superior Chippewa Reserva- A A’ James A. Berg tion extending into St. Louis County. 1 6 3 2 The surficial sand aquifer shown on Figure 1 consists of water-saturated, unconsolidated sand and k gravel. This aquifer is a relatively minor direct source of human water supply for domestic and municipal wells. roo B 2011 Mar River Only eight percent of the approximately 3500 wells in the mapped area draw water from this aquifer; the Martin tin Lake e Jo remaining wells rely on water from buried sand and gravel and bedrock sources. The surficial sand aquifer is, however, a vital source of water for most aquatic habitats of rivers, lakes, and wetlands within the extent of this aquifer. Furthermore, this aquifer is the most important recharge source for the underlying buried sand and 92°30' gravel and bedrock aquifers. LOCATION DIAGRAM R. 17 W. ARROWHEAD STONEY BROOK 18 DATA SOURCES T. 50 N. Well data from the database of well logs (County Well Index [CWI]) maintained by the Minnesota Twin SCALE 1:100 000 FOND DU LAC BAND BREVATOR Geological Survey (MGS) and the Minnesota Department of Health (MDH) provided much of the information COMPILATION SCALE 1:100 000 Lakes used to produce the maps, cross sections, and tables of this atlas. Electrical resistivity surveys were conducted at nine locations (shown as short magenta lines, Figure 1) to determine the thickness of surficial sand and gravel B Lost B’ 1 0 1 2 3 4 5 MILES Lake deposits. The electrical resistivity surveys were conducted to fill in data gaps where well records or other drill Simian hole data were rare or absent. The sand and gravel was detected by its resistivity difference from other material. 1 0 1 2 3 4 5 6 7 8 9 KILOMETERS Brook Lake Creek The base of the surficial sand and gravel deposit is interpreted as an abrupt change from the higher electrical 36 31OF LAKE SUPERIOR resistivity values of the sand and gravel to the lower resistivity values of the clay and silt of the underlying 34 36 92°45' 31 Y 93°00' fine-grained glacial materials. T ST. LOUIS COUNTY ST. LOUIS COUNTY N R. 21 W. R. 20 W. R. 16 W. U Hardwood O Lake CHARACTERISTICS OF SAND AND GRAVEL AQUIFERS C Elm 1 6 N 1 S I Creek 6 1 t 6 6 H 6 . 1 K a 1 s Simian 6 L 1 T t y o I Depositional History of the Surficial Sand u A i CHIPPEWA RESERVATION s 46°45' 46°45' Dead Fish )33 Lake Creek Figure 1 shows the distribution and thickness of surficial sand deposits in the study area. The geologic history of surficial sand deposition is derived from descriptions on Plates 3 and 4 of Part A. Most of the surficial Little Cedar R Lake iv e sand deposits shown in Figure 1 are from outwash deposits of several phases of advance and retreat of the Supe- r T amarack Brook River rior ice lobe, which advanced into the area from the present-day area of Lake Superior. The oldest of these 73 Cloquet River ) deposits are associated with the St. Croix phase and occur in the northern and western portions of the Fond du Miller y Cross y Lake one Lac Reservation with other scattered occurrences in the northwestern portion of the county. A subsequent ice Lake RED CLOVER PROGRESS St CLOQUET Midwa T. 49 N. PERCH LAKE aw THOMSON lobe advance and retreat, called the Split Rock phase, deposited much of the surficial sand and gravel in the T. 49 N. Squ C First C’ southeastern portion of the Fond du Lac Reservation and extending two to three miles south of the southern Lake BESEMAN Third Fond du Lac Reservation boundary. The complex southwest-northeast trending series of sand and gravel depos- Lake its that underlie and surround the Moose Horn River in the south-central portion of the county and Otter Creek ¤61 in the northeast portion were deposited in outwash diversion channels as the Superior ice lobe advanced and Rice Big Esko Portage Creek 35 Lake Perch ¦§ then retreated during the Nickerson Phase. Thick sand and gravel deposits southeast of these diversion channels Otter were also deposited during this phase. During the latest stages of this retreat, glacial Lake Superior formed with Y a shoreline much farther to the southwest than the present day Lake Superior. The thinner sand deposits in the Lake T 31 N U southeastern portion of Carlton County that roughly surround the Nemadji River drainage were near-shore and 31 31 36 36 31 36 36 36 31 k O Woodbury Lake e e 31 9000 C deltaic deposits of glacial Lake Superior. 36 D Lake Jaskari r D’ C S Lake I U Wild Little O L Aquifer Specific Capacity and Hydraulic Conductivity )210 Rice Gill r . amarack e 6 6 T Cromwell 1 Sawyer Lake t River T 1 t 1 n 6 r Th mso R o S 1 6 6 6 O Creek Wright i Island 1 e v v Reservoir e 1 r Lake Ri Estimating the yield of groundwater from an aquifer requires information about an aquifer’s extent and 210 ) Torchlight C saturated thickness, hydraulic conductivity (ability to transmit water), and other information about the ground- reek Tamarack le Lake Cole tt 210 water system, such as the relationship to recharge sources and other aquifers. The map of the surficial sand e Carlton ) Y Lake K Lake r 7 T Little te River N t N I aquifer on this plate (Figure 1) and Figures 3 through 11 on Plate 5 of Part A provide aquifer extent and thick- Creek O St. Louis U S O ness. Data to estimate aquifer specific capacity and hydraulic conductivity are obtained by pumping water from N C r e t O E t S E’ a well at a constant rate for a certain period of time. The simplest test of this type, the specific capacity test, is O A Eagle Creek Creek 23 C Silver ) L S M I Lake Merwin G defined as well discharge, measured in gallons per minute, divided by feet of water-level drawdown (gpm/ft) in o T. 48 N. Mattlia Lake o U s W Walli Lake e Little Otter O the pumped well. Generally the well is pumped for a limited amount of time, such as an hour. High well specific River r D Lake ve Bob Horn Ri Lake Jay Cooke T. 48 N. capacity values indicate that large amounts of groundwater can be withdrawn with limited water-level draw- K State Park ettle down in the well. In addition, a high well specific capacity value usually indicates the aquifer has a high hydrau- W Kettle Chub e LAKEVIEW EAGLE Lake CORONA TWIN LAKES SILVER BROOK s lic conductivity value. t ATKINSON Lake Park Limited specific capacity data were available for the mapped area (Table 1). The data in Table 1 were Wrenshall Lake Venoah grouped by general aquifer type including the surficial sand aquifer that is shown on this plate, buried sand and Br Lake an ch gravel aquifers (Plate 9), and the Fond du Lac aquifer. Data from other bedrock aquifers were not available. Wells in the surficial sand and buried sand and gravel aquifers have much higher specific capacities than wells Lac in the Fond du Lac aquifer; their higher specific capacities indicate that these aquifers, where they are present P Hay 31 a La Belle rk Lake 31 31 31 36 31 Heikkila 36 36 36 in the mapped area, might be better water sources. 36 31 L a 31 ke 36 3000 Table 2 is a summary of available aquifer test data in the mapped area. This type of test requires pump- F F’ ing the well for a longer period of time than the specific capacity tests. These data are from municipal and C re Creek e public water supply wells in Barnum, Kettle River, Moose Lake, Moose Lake correctional facility, Carlton, and k ¤61 6 1 6 1 6 1 6 1 6 1 1 6 Clear 6 Cloquet. These data show that the hydraulic conductivity values of the surficial sand and buried sand and gravel Bear Creek Lake aquifers are roughly comparable, with the surficial sand aquifer having somewhat higher values. Flodin 73 K iver Lake ) in R Mahtowa g Mud Water Table Elevation and Depth W Hizer e B s Lake Ellstrom t Lake la c K khoo The mapped area is within four major surface watersheds (Figure 2): Mississippi River (Grand Rapids), ettle Fo D Creek rk 35 e St.