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Introduction

In 2005, about 33.8 million gallons per day (Mgal/d) was withdrawn from water sources in Natchitoches Parish, Louisiana (fig. 1). Surface water sources accounted for about 86 percent (29.2 Mgal/d) of all withdrawals whereas groundwater sources accounted for about 14 percent (4.62 Mgal/d) (table 1). Withdrawals for industrial use accounted for about 42 percent (14.1 Mgal/d) of the total

Location of study area, Natchitoches Parish, Louisiana. (Note, the Black Lake reservoir comprises Black Lake and Clear Lake.)

Figure 1. Location of study area, Natchitoches Parish, Louisiana. (Note, the Black Lake reservoir comprises Black Lake and Clear Lake.)

water withdrawn (table 2). Other categories of use included public supply, rural domestic, livestock, rice irrigation, general irrigation, and aquaculture. The city of Natchitoches used almost 5.6 Mgal/d (about 5.2 Mgal/d of surface water and 0.4 Mgal/d of ground water) for public supply. Water-use data collected at 5-year intervals from 1960 to 2005 indicated that total water withdrawals increased from about 3.5 Mgal/d in 1960 to a peak of almost 35 Mgal/d in 2000 (fig. 2).

Water withdrawals in Natchitotches Parish, Louisiana, 1960–2005

Figure 2. Water withdrawals in Natchitotches Parish, Louisiana, 1960–2005.

This fact sheet summarizes basic information on the water resources of Natchitoches Parish. Information on groundwater and surface-water availability, quality, development, use, and trends is based on previously published reports listed in the Selected References section.

Groundwater Resources

The primary groundwater resources of Natchitoches Parish, from near surface to deepest, include the Red River alluvial, upland terrace, Sparta, and Carrizo-Wilcox aquifers (fig. 3). The Catahoula and Cockfield aquifers are also sources of freshwater in some parts of the parish (table 1) but are not considered major resources because of their limited extents within the parish; consequently, they are not discussed in this report. Fresh groundwater (water with a chloride concentration of less than 250 milligrams per liter [mg/L]) is available throughout the parish at depths ranging from near land surface to about 2,000 feet (ft) below the National Geodetic Vertical Datum of 1929 (NGVD 29) in the southwestern part of the parish (fig. 1).

Generalized west-to-east hydrogeologic section through Natchitoches Parish, Louisiana (modified from Smoot, 1989)

Figure 3. Generalized west-to-east hydrogeologic section through Natchitoches Parish, Louisiana (modified from Smoot, 1989). Trace of section shown on figure 1.

Recharge to aquifers is from rainfall, leakage from adjacent aquifers, and rivers during periods of high flow. Discharge from the aquifers is by natural flow into rivers during periods of low flow, leakage into underlying aquifers, and withdrawal from wells.

State well-registration records listed 876 active water wells in Natchitoches Parish in 2010, including 671 domestic, 115 irrigation, 75 public-supply, and 15 industrial use wells. In 2005, groundwater withdrawals for various uses included public supply, rural domestic, livestock, rice irrigation, general irrigation, and aquaculture (table 2).

Red River Alluvial Aquifer

The Red River alluvial aquifer is the most heavily pumped aquifer in Natchitoches Parish. The aquifer consists of gray and brown poorly-sorted sand and gravel and covers about a third of the parish. The Red River alluvial aquifer trends toward the southeast, through the central portion of the parish. It underlies the present course of the Red River and has a maximum width of about 16 miles (mi). A few miles south of the city of Natchitoches, the Red River is near the eastern boundary of the aquifer. In Natchitoches Parish, the maximum thickness of the Red River alluvial aquifer is about 60 ft, with an average thickness of about 45 ft.

Saltwater is present in the Red River alluvial aquifer in a few localized areas in Natchitoches Parish where highly mineralized water from underlying aquifers is discharged into the alluvial aquifer. Where saltwater is present, however, it is stratified with freshwater at shallower depths overlying saltwater at the base of the aquifer (fig. 3).

Recharge to the aquifer is from rainfall, leakage from adjacent aquifers, and the waters of Cane River Lake. Water levels in the alluvial aquifer fluctuate primarily in response to the stage of the Red River and precipitation. The hydrograph for well Na-474, which is located near the City of Natchitoches, shows seasonal water-level fluctuations of about 6 to 8 feet (ft) during the period 1989–2010 (fig. 4). Flow in the aquifer is generally towards the Red River with a southerly (down valley) component of flow.

Water levels in well Na-474 screened in the Red River alluvial aquifer and well Na-487 screened in the Wilcox aquifer in Natchitoches Parish, Louisiana (see fig. 1 for well locations) (U.S. Geological Survey, 2012a)

Figure 4. Water levels in well Na-474 screened in the Red River alluvial aquifer and well Na-487 screened in the Wilcox aquifer in Natchitoches Parish, Louisiana (see fig. 1 for well locations) (U.S. Geological Survey, 2012a). Land surface is measured in feet (ft) above the National Geodetic Vertical Datum of 1929 (NGVD 29).

State well-registration records listed 146 active wells screened in the Red River alluvial aquifer in Natchitoches Parish in 2010, including 70 domestic, 67 irrigation, 5 industrial, and 4 public-supply wells. Depths of these wells ranged from 17 to 150 ft below land surface with a median well depth of 85 ft. Yields from wells screened in the Red River alluvial aquifer in Natchitoches Parish range from 1 to 1,500 gallons per minute (gal/min) with most yields (73 percent) less than 80 gal/min. In 2005, groundwater withdrawals from the Red River alluvial aquifer in Natchitoches Parish totaled about 2.65 Mgal/d, primarily for rural domestic use and irrigation.

A statistical summary of selected water-quality characteristics for freshwater samples collected from 101 wells screened in the Red River alluvial aquifer in Natchitoches Parish is listed in table 3. Based on median values for hardness, water from the Red River alluvial aquifer is generally very hard. Water in less than one-third (31 percent) of the sampled wells was below the U.S. Environmental Protection Agency’s (EPA) Secondary Maximum Contaminant Level (SMCL) of 500 mg/L for dissolved solids concentration. Water from the aquifer generally does not exceed the SMCLs for pH, color, and chloride concentrations but generally exceeds the SMCLs of 300 micrograms per liter (μg/L) for iron concentrations and 50 μg/L for manganese concentrations.

Upland Terrace Aquifer

The upland terrace aquifer, consisting of clay, sand, and gravel, covers only about 10 percent of the parish. The aquifer is principally located in the northern part of the parish between the Red River and the chain formed by Black Lake and Clear Lake (fig. 1). Sands are generally yellow or gray at depth, and red in weathered outcrops. The thickness of these deposits probably does not exceed 100 ft, with an average thickness of about 50 ft. Water levels in the aquifer fluctuate rapidly and through a considerable range in response to rainfall.

State well-registration records listed 128 active wells screened in the upland terrace aquifer in Natchitoches Parish in 2010, including 116 domestic, 8 public supply, 2 irrigation, and 2 industrial wells. Depths of these wells ranged from 12 to 125 ft below land surface with a median well depth of 56 ft. Yields from wells screened in the upland terrace aquifer in Natchitoches Parish range from 5 to 255 gal/min. In 2005, groundwater withdrawals from the upland terrace aquifer in Natchitoches Parish totaled about 0.12 Mgal/d, primarily for rural domestic use.

Because few water-quality data are available for the upland terrace aquifer in Natchitoches Parish, water quality is not discussed in this report.

Sparta Aquifer

The Sparta aquifer generally underlies the southern half of Natchitoches Parish and is present along the northeastern parish line. The Sparta aquifer outcrops in a narrow band in the northeast and central portion of the parish and consists of light gray sand and clay. Grain size varies from fine sand to coarse sand. The thickness of the aquifer in Natchitoches Parish ranges from about 250 ft to more than 600 ft. Individual sand beds in the lower part of the Sparta aquifer are as much as 250 ft thick. Groundwater flow is generally downdip to the south and east. Freshwater is present in the Sparta aquifer in northeastern Natchitoches Parish and in a 5- to 10- mi-wide band extending southwest from the southern end of Saline Lake into Sabine Parish. Saltwater is present in the Sparta aquifer in most southern and southeastern areas of Natchitoches Parish.

State well-registration records listed 54 active wells screened in the Sparta aquifer in Natchitoches Parish in 2010, including 43 domestic, 10 public supply, and 1 irrigation well. Depths of these wells ranged from 15 to 725 ft below land surface with a median well depth of 145 ft. Yields from wells screened in the aquifer in the parish range from 4 to 365 gal/ min. In 2005, groundwater withdrawals from the Sparta aquifer in Natchitoches Parish totaled about 0.50 Mgal/d, primarily for public supply.

A statistical summary of selected water-quality characteristics for water samples collected from 30 wells screened in freshwater areas of the Sparta aquifer in Natchitoches Parish is listed in table 3. Based on median values, water from the Sparta aquifer is generally soft and generally does not exceed SMCLs for pH, color, and iron and dissolved solids concentrations. Water in some areas, however, may exceed the SMCLs for iron or manganese.

Carrizo-Wilcox Aquifer

The Carrizo-Wilcox aquifer underlies all of Natchitoches Parish and outcrops north of Black Creek in the northwest part of the parish and west of the city of Natchitoches in the western part of the parish. The Carrizo Sand is a discontinuous, massive sand that overlies the eroded surface of the Wilcox aquifer. Regionally, the Carrizo Sand and the Wilcox aquifer are hydraulically connected, and the units are combined into one aquifer. The Carrizo Sand consists of light colored, fine to medium grained material with an average thickness of about 75 ft in the parish. Sands in the Wilcox aquifer are interbedded with dark clay and generally are fine grained, homogeneous, and typically dark, almost black in many places, because of the lignite and glauconite in the formation.

The total thickness of the Carrizo-Wilcox aquifer in Natchitoches Parish ranges from about 300 to 3,700 ft, but the thicknesses of the individual sand beds within the aquifer generally range from about 1 ft to more than 100 ft. Freshwater in the Carrizo-Wilcox aquifer is generally present in the northern two-thirds of the parish; however, saltwater is present in the aquifer under most of the Red River Valley.

Groundwater-level data from 1991 indicated water levels in the aquifer ranged from about 180 ft above NGVD 29 along the western parish line to less than 100 ft NGVD in the Red River Valley. Groundwater flow in the Carrizo-Wilcox aquifer is generally toward the Red River. Data from well Na-487 (fig. 4), screened in the Carrizo-Wilcox aquifer, showed decreasing water levels from 2002 to 2010. The well is located in the western part of the parish near Robeline (fig. 1), and is 445 ft deep.

State well-registration records listed 342 active wells screened in the Carrizo-Wilcox aquifer in Natchitoches Parish in 2010, including 267 domestic, 41 public supply, 29 irrigation, and 5 industrial wells. Depths of these wells ranged from 20 to 612 ft below land surface with a median well depth of 187 ft. Yields from wells screened in the aquifer in the parish range from 1 to 667 gal/min. In 2005, groundwater withdrawals from the Carrizo-Wilcox aquifer in the parish totaled about 1.23 Mgal/d, primarily for public supply, irrigation, and domestic use.

A statistical summary of selected water-quality characteristics for water samples collected from 69 wells screened in freshwater areas of the Carrizo-Wilcox aquifer in Natchitoches Parish is listed in table 3. Based on median values, water from the Carrizo-Wilcox aquifer generally is soft and does not exceed the SMCLs for pH, and chloride, iron, and manganese concentrations. Water in the Carrizo-Wilcox aquifer generally exceeds the SMCLs for color and dissolved solids concentrations.

Surface-Water Resources

In 2005, about 29.2 Mgal/d of surface water was withdrawn in Natchitoches Parish for public supply, industrial, rice irrigation, general irrigation, and aquaculture uses (table 2). Primary sources of fresh surface water in Natchitoches Parish include the Red River, Sibley Lake, Bayou Pierre, Little River, Black Lake reservoir, and Cane River (table 1). Other major streams in the parish include Kisatchie Bayou and Saline Bayou.

About 12.9 Mgal/d of surface water were withdrawn from the Red River in 2005 (table 1). A series of 5 locks and dams, including Lock and Dam 3 near Colfax and Lock and Dam 4 near Coushatta (fig. 1), control flow on the Red River in Louisiana. The average discharge of the Red River at Alexandria, about 25 mi south of Natchitoches Parish, is about 30,900 cubic feet per second. Water samples analyzed from 1995 to 2000 indicated that water in the Red River at Grand Ecore (station number 07351930) (fig. 1) generally is hard (table

4) and does not exceed the SMCLs for pH and chloride and

sulfate concentrations. Iron concentration data are not available. Dissolved oxygen is generally greater than 5 mg/L, which is considered the minimum value for a diversified population of fresh, warm-water biota, including sport fish (Louisiana Department of Environmental Quality, 2008).

About 3.17 Mgal/d of water were withdrawn from Bayou Pierre in 2005 (table 1). The average discharge in Bayou Pierre near Lake End (station number 07351750) (fig. 1) was 992 cubic feet per second from October 1980 through September 2009, and the drainage area is about 860 square miles (mi) (U.S. Geological Survey, 2012b). Water samples analyzed from 1995 to 2000 indicated that water in Bayou Pierre near Lake End generally is hard (table 4) and does not exceed the SMCLs for pH and chloride, sulfate, and iron concentrations. Dissolvedoxygen concentrations generally are greater than 5 mg/L.

Water samples from Saline Bayou collected from 1953 to 1978 near Clarence indicated that the water generally is soft (table 4) and does not exceed the SMCLs for pH and chloride and sulfate concentrations. The drainage area of Saline Bayou near Clarence (station number 07353000) is 1,386 mi.

Black Lake reservoir, located on Black Bayou, consists of two interconnected lakes: Black Lake and Clear Lake. The reservoir was completed in 1934; however, some subsequent work was done in 1949. At 100-ft elevation, the reservoir drains 920 mi , has a surface area of 20.17 mi, and has an average depth of about 8 ft. Most of Black Lake is thick with trees and other vegetation whereas Clear Lake is mostly open water. The reservoir is widely used for recreation. The water in Black Lake reservoir is generally of good quality. During the summer, however, oxygen concentrations at the bottom of the reservoir may become depleted, and hydrogen sulfide, iron, and manganese concentrations may increase to nuisance levels (Shampine, 1971).

Selected References

This fact sheet was published by the U.S. Geological Survey, in cooperation with the Louisiana Department of Transportation and Development (DOTD). Thanks are given to Zahir “Bo” Bolourchi, Director, Water Resources Programs, Louisiana Department of Transportation and Development, who contributed to the content and design of the fact sheet.

By Robert B. Fendick, Jr., Lawrence B. Prakken, and Jason M. Griffith

For additional information, contact:

Director, USGS Louisiana Water Science Center 3535 S. Sherwood Forest Blvd., Suite 120 Baton Rouge, LA 70816 E-mail: dc_la@usgs.gov Fax: (225) 298–5490 Telephone: (225) 298–5481 Home Page: http://la.water.usgs.gov

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This page was imported from U.S. Geological Survey. Published by the U.S. Geological Survey and, as a work of the United States government, in the public domain.

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