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(1974) Chlorine Residue Study, Barton Springs Creek, Austin, Texas

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TXHD17.pdf 4 pages completed 14 entities

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--- Page 1 --- CHLORINE RESIDUE STUDY BARTON SPRINGS CREEK AUSTIN, TEXAS Thomas E. Chandler August 4, 1974 --- Page 2 --- INTRODUCTION Barton Springs a is fed by a cold water spring with profuse vegetation in the creek bottom. The bottom consists of bedrock, sand and gravel with deeper areas covered with silt. The Texas Parks and Wildlife Department has recently stocked the area below the dam of the Barton Springs Swimming Pool. Concern was expressed over the possible lethal levels of chlorine added to the creek every Monday and Thursday nights through the summer. Each Monday and Thursday night the pool is drained and the bottom washed off with a high pressure hose. Then the sides and bottom are sprayed with a mix- ture of HTH and water (approximately 5 - 7% lbs. to 300 gals. water). During this spraying operation, the gates to the dam are left open. After completion of the spraying, the gates are closed and the pool allowed to refill about 14 - 2 hours. This study was conducted to deter- mine the concentration levels of chlorine reaching the creek during the chlorination process. METHODS AND MATERIALS Four stations were chosen on August 22, 1974 prior to chlorination to determine dissolved oxygen, pH, conductivity and chlorine. Station one was located immediately below the Barton Creek Pool Dam. Station two was located across from the canoe concession (approximately 300 yds. downstream). Station three was located beneath the Barton Springs Road Bridge. Station four was located approximately 400 - 500 yds. down- stream from station three and just before Barton Springs Creek merges with Town Lake. --- Page 3 --- After the first sampling run, before chlorination, ennertiaes samples were taken at station one every fifteen minutes for two hours and then changed to every thirty minutes for another two hours. If chlorine con- centrations reached lethal levels at station one, other chlorine tests would be run to determine the progress of chlorine residue traveling downstream. Dissolved oxygen was measured with a Delta model 75X dissolved oxygen meter. The pH was measured with a Beckman Electromate Portable pH meter. Specific conductivity was measured with Beckman RA-2A portable conductivity meter. Chlorine samples were run by using a Delta Model 50 portable laboratory. Temperature was measured with a hand-held glass thermometer. TABLE OF RESULTS Specific Station Time D.O. cl pH Cond. Temp. 1 1920 7.9 BDL 7.5 584 23°C 2 1955 6.0 BDL 7.2 584 25°C 3 2015 4.7 BDL 7.2 584 23°C 4 2025 5.3 BDL Tez 584 23°C Wind - Calm BDL - below detectable limits Pool being lowered DISCUSSION Chlorine levels were essentially negative (below detectable limits) throughout the duration of the study. One sample just prior to closing the gate had a reading of "one" on the meter. This was adjusted to a concentration level of 0.025 ppm chlorine from the standard curve sup- plied with this instrument. rw --- Page 4 --- The conclusion reached is that the chlorine residue levels in Barton Springs Creek below the swimming pool are not in high enough con- centrations to be lethal to the exotic fishes stocked by the Department.

Detected Entities

location (8)

AUSTIN 0.999 p.1 AUSTIN, TEXAS
Barton Creek Pool Dam 0.999 p.2 Station one was located immediately below the Barton Creek Pool Dam
Barton Springs 0.999 p.2 Barton Springs a is fed by a cold water spring
Barton Springs Creek 0.999 p.1 CHLORINE RESIDUE STUDY BARTON SPRINGS CREEK
Barton Springs Road Bridge 0.999 p.2 Station three was located beneath the Barton Springs Road Bridge
Barton Springs Swimming Pool 0.999 p.2 the area below the dam of the Barton Springs Swimming Pool
Town Lake 0.999 p.2 just before Barton Springs Creek merges with Town Lake
Barton Creek 0.850 p.2 ...and chlorine. Station one was located immediately below the Barton Creek Pool Dam. Station two was located across fr…

organization (5)

Texas Parks and Wildlife Department 0.999 p.2 The Texas Parks and Wildlife Department has recently stocked
Beckman Electromate 0.800 p.3 The pH was measured with a Beckman Electromate Portable
Beckman RA-2A 0.800 p.3 Specific conductivity was measured with Beckman RA-2A portable
Delta Model 50 0.800 p.3 Chlorine samples were run by using a Delta Model 50 portable
Delta model 75X 0.800 p.3 Dissolved oxygen was measured with a Delta model 75X dissolved

person (1)

Thomas E. Chandler 0.999 p.1 Thomas E. Chandler August 4, 1974