APPENDIX H

 

Spatial Analysis of Choctaw Creek Subwatershed

Reach I ) Red River Basin

Grayson County, Texas

 

BASIN SUMMARY REPORT

FOR THE

RED RIVER BASIN

September 1999

 

 

 

1.0  Background

 

Reach I of the Red River Basin (eastern region) was monitored by the Authority in FY 1997.  During this period, it was necessary to choose priority subwatersheds to conduct further study of concerns identified during previous assessments.  Therefore, subwatersheds in Reach I of the Red River Basin were analyzed for many factors to determine which would be classified as priority subwatersheds.  Choctaw Creek, Bois D’Arc Creek and Pine Creek subwatersheds were chosen as the three priority subwatersheds in this reach.  These perennial creeks have relatively large watersheds containing all major land uses including urban, farming and ranching activities.  All three creeks receive a large amount of wastewater effluent from major discharges in the reach.

 

Choctaw Creek was chosen as the highest priority of the three watersheds since it is an unclassified stream and the watershed encompasses a large urban area of Sherman with several industrial companies which tend to increase the potential for water quality problems through runoff, spills, leaks, etc.  The City of Sherman discharges its wastewater effluent into a tributary of Choctaw Creek, contributing considerable flow to the watershed.  Additionally, there are numerous petroleum storage tanks and groundwater wells which add to the potential of water quality problems.

 

Historical water quality data shows several fish kills in Choctaw Creek having several different causes.  These causes include sewage, pesticides and ammonia.  This indicates that at least in the past, undesired pollutants are finding their way into Choctaw Creek.  Monitoring results taken by the Authority showed elevated levels of total dissolved solids and nutrients for Choctaw Creek.  All these factors resulted in the selection of the Choctaw Creek watershed as the highest priority watershed in Reach I of the Red River.

 

2.0  Trend Analysis

 

Trend analysis of chemical constituents found to be a concern or possible concern in the 1996 screening process which was performed on stations located in the selected subwatershed with sufficient data.  As seen on the following tables, there were no significant trends found for the 12 constituents analyzed for the two stations having sufficient data.


3.0  Identifying Sources

 

Global positioning data were collected on petroleum storage tanks (PSTs) and groundwater wells were taken to obtain accurate locations on potential sources of pollution which would have the greatest influence on the priority watershed.  Maps were then prepared showing the geographical location of these potential sources of pollution, as well as the location of municipal landfills.

 

4.0  Events and Issues

 

Events identified in this subwatershed include two permit amendments for the City of Sherman WWTP dated 11/21/97 and 2/24/98, as well as six reported fish kills listed below:

 

 

Date

Estimate Killed

Source

General Cause

Specific Cause

Location

 

5/25/77

 

28

 

Municipal

Organic

Compound

 

Sewage

Choctaw Creek ) Northwest Corner

of Grayson County between

FM 1753 and SH 120

6/25/83

Unknown

Municipal

Organic Compound

Sewage

Choctaw Creek at FM 120

6/10/87

20

Individual

Organic Compound

Other

Choctaw Creek ) Grayson County

5/30/90

100

Agriculture

Organic Compound

Pesticide

Choctaw Creek near FM 697 and FM 11

 

9/17/94

 

500

 

Municipal

Low Dissolved Oxygen

Sewage Bypass

 

Post Oak Creek at Discharge

9/23/94

50

Industry

Inorganic Compound

Ammonia

Choctaw Creek at Discharge from

Oscar Meyer plant

 

 

These reported fish kills show that all major land uses in the subwatershed have had a negative effect on water quality.

 

 

5.0       Statistical Analysis

 

Statistical analysis of chemical constituents found to be a concern was performed on two TNRCC monitoring sites.  Other sites were not adequate for analysis due to certain factors.


 

 

Station

Number

Events

Date Range

# of Days

Determination

10108

2

5/23/1984

1

Insufficient Data

10109

11

5/23/1984 – 7/23/1991

3

Timespan Inadequate

10110

10

5/29/1991 – 7/23/1991

2

Timespan Inadequate

10111

20

5/23/1984 – 4/15/1992

10

Adequate Data for Analysis

10112

4

5/23/1984 – 7/23/1991

2

Insufficient Data

10114

2

5/23/1984

1

Insufficient Data

10115

24

5/23/1984 – 12/27/1998

15

Adequate Data for Analysis

15442

N/A

N/A

N/A

Insufficient Data

15446

N/A

N/A

N/A

Insufficient Data

16123

8

8/21/1997 – 3/20/1998

8

Insufficient Data

 

 

 

Statistical Analysis for Station 10111

 

Parameters

N

P-Value

00300

16

0.798971

00620

10

0.404762

00650

N/A

N/A

00665

10

0.736605

00671

10

0.991070

00900

N/A

N/A

00940

10

0.878393

00945

10

0.682449

01025

N/A

N/A

01049

N/A

N/A

01075

N/A

N/A

70507

N/A

N/A

 


 

Statistical Analysis for Station 10115

 

Parameters

N

P-value

00300

20

0.943958

00620

N/A

N/A

00650

N/A

N/A

00665

N/A

N/A

00671

N/A

N/A

00900

N/A

N/A

00940

N/A

N/A

00945

N/A

N/A

01025

N/A

N/A

01049

N/A

N/A

01075

N/A

N/A

70507

N/A

N/A

 

Map of Choctaw Subwatershed (Transportation Theme)

 

Map of Choctaw Subwatershed (Hydrology Theme)

 

Map of Choctaw Subwatershed (City Boundary Theme)

 

Map of Choctaw Subwatershed (TNRCC Monitoring Stations Theme)

 

Map of Choctaw Subwatershed (Miscellaneous Theme)

 

Map of Choctaw Subwatershed (Water Resources I Theme)

 

Map of Choctaw Subwatershed (Water Resources II Theme)

 

Graph of Choctaw Creek at SH 11 SE of Sherman – Dissolved Oxygen Measurements

 

Graph of Choctaw Creek at SH 11 SE of Sherman – Chloride and Sulfate Measurements

 

Graph of Choctaw Creek at SH 11 SE of Sherman – Nitrate + Nitrite, Dissolved Orthophosphorus Measurements

 

Graph of Choctaw Creek at SH 11 SE of Sherman – Total Phosphorus, and Post Oak Creek at FM 1417, SE of Sherman, Dissolved Oxygen