TPWD 1964 F-7-R-12 #947: Fisheries Investigations and Surveys of the Waters of Region 1-A, Job No. C-1: Pollution Studies
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JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-7-R-12
FISHERIES INVESTIGATIONS AND SURVEYS OF THE WATERS 0F REGION l-A
Job No. C-l‘ Pollution Studies
Project Co-leaders: Lonnie J. Peters, Region 1-Al -
- George G. Henderson, Jr., Region l-Ai
J. Weldon Watson
Executive Director
Parks and Wildlife Department
Austin, TeXas
Marion Toole Eugene A.Wa1ker
.D-J Coordinator Assistant Director, Wildlife
March 9, 1965
ABSTRACT
W
Pollution from the Canyon sewage treatment plant killed fish in approximately
3 miles of Tierra Blanca Creek. Future pollution from this source could be pre-
vented if the plant effluent was used for irrigation of nearby fields instead of
being released into the creek.
A serious threat to the fish population of Buffalo Lake exists in the
accumulation of organic materials in feed lots located in the Hereford_area.
Run-off from these feed lots carries a tremendous organic load and results in a
"slugging" of oxygen-depleted water which destroys aquatic life downstream in
Tierra Blanca Greek and the upper end of Buffalo Lake. Other continuing sources
of pollution are the Hereford sewage treatment plant and the slaughterhouse.
Seasonally, vegetable processing houses contribute to the organic load.
Region 1-A2 (SlatOnl
Fish mortalities were investigated at four lakes this year. At Buffalo
Springs Lake there was a fish die-off of almost 3 months duration. The mortalities
progressed at varying rates and sepsratewspecies died at different times of the
year; The suspected cause is poor basic water quality and a thermally deve10ped
toxic layer of chemicals which existed in the lake most of the summer.
Reese Air Force Base Lake had a continuing or recurring die-off which was
attributed to poor water quality in combination with insecticide buildup in
fish and wide fluctuations of dissolved oxygen and carbon dioxide gases.
The fish died at McKenzie State Park Lake because of unusually high water
temperatures associated with extremely high dissolved oxygen and low carbon
dioxide levels.
Fish mortalities at South Lake are unexplained. Circumstantial evidence
indicated that an angler had attempted to stock the lake with large fish which
did not survive.
The site of a proposed flood control plays lake drainage project at Plainview
was examined. Polluting wastes were being discharged into one of the plays lakes.
It was recommended that business establishments be required to treat these
wastes prior to their admission to the watershed.
JOB COMPLETION REPORT
State of Texas
Project No. F-7-R-12 _ Name: _§i§he£le§_lnggstigatiggs and Sggggys of the
Hammettesiemljnmww
Job No. 0-1 ____‘ Title? Bollg£i2g_§tugie§m£Fisheries Region l-A-l!
Period Covered ____ __ JQBEBFX 1r_la9a_;_aeseaag:_gl._1293_"_______
Objectives:
To determine the source and nature of natural or man~made pollutants which
affect fish populations.
Procedure:
Field observations and limited water analyses were by project personnel.
Laboratory analysis for pH, conductivity, dissolved solids, chlorides, sulfates,
chlorine demand, dissolved oxygen, B.O.D., ammonia nitrogen, nitrite nitrogen,
nitrate nitrogen, alkalinity, and suspended solids were made by the State Health
Department laboratory. Additional laboratory analyses for dissolved oxygen,
A.B.S., and B.O.D. were made by the Potter-Randall County Health Unit.
A11 fish kills discovered by, or reported to, project personnel were in-
vestigated to determine if they were caused by pollution. If pollution was
apparent, attempts were made to locate the sourcefis) and to determine the nature.
Findings:
During this segment, pollution-caused fish kills were detected along two
areas of Tierra Blanca Creek in Randall and Deaf Smith counties. An area of
the creek, beginning at the Canyon city sewage treatment plant and extending
downstream for about 3 miles. did not receive normal run-off during an extended
period of drought and became stagnant in late February 1964. Fish began dying
at this time (primarily gizzard shad. DQEQEQEQHEéflfiflléflflflln but observations and
D.O. checks did not indicate pollution. The creek was very low, and extremely
cold water suggested the possibility of normal winter mortality. Water samples
collected along this portion of Pierre Blanca Creek on March 3, 1964, were
analyzed for D.0., A.B.S., and B.O.D. at the Potter-Randall County Health Unit
laboratory. Results, shown in Table l and Figure 1, revealed a high B.O.D. in
all samples. Fish continued to die throughout March, and on April 13 a second
investigation was made. Analyses of water samples taken during this check also
revealed excessive B.O.D. and critically low D.O.
By mid-June, still no run-off had entered the creek, and a major fish kill
occurred due to oxygen depletion. Recommendations were made to the Canyon city‘
manager to provide for disposal of the sewage plant‘s effluent other than release
into Tierra Blanca Creek.
Table 1. Analysis Results of Water Samples from Tierra Blanca Creek, March 3, 1964.
goint of Collection D.0. A.B.§. B.O.D.
l. .1 mile above sewage plant (Canyon) 7.3 Trace 28
2. Final effluent at plant 2.9 6 55
3. Oxidation pond 3.7 . 8 53
4. Greek at oxidation pond effluent 4.1 6 48
5. Creek at Highway 217 3.8 .'6 47
6. Palo Duro Club Lake #1 4.6 5 25
7. Palo Duro Club Lake #2 4.8 5 12
8. Palo Duro Club spillway 5.2 3 l7
A second fish-kill, of greater magnitude, occurred in Tierra Blanca Creek
downstream from Hereford and extended into the upper end of Buffalo Lake. Heavy
rains in the Hereford area washed organic material from feed lots into the creek
where it was carried downstream, reaching the lake about 25 hours after the
initial inflow of run-off into the lake. Fish ascending the creek were met by
'the polluted, oxygen-depleted water and were killed. '
Project persOnnel were at Buffalo Lake on both Saturday, June 13, and Sunday,
June 14, gathering data concerning fish spawning activities. -A moderate flow of
fresh, unpolluted water was entering the lake at this time. On Monday, June 15,
at 8:30 a.m. project personnel approaching the extreme upper end of the lake-ob-
lserved sick fish and noted a strong "feed-lot" odor. Continuing upstream into
Tierra Blanca Creek, increasing numbers of sick and dying fish-were noted. It
appeared that the polluted water had first reached the lake only a short time
earlier, probably around 6 a.m. By noon on Monday, June 15, thousands of dead
fish (mostly small carp and bullheads) were washed ashore along the creek banks
and in the upper area of the lake which had received the pollution. Damage to
game species appeared minimal, probably because-the inflow was considerably cOlder
than the lake water, and channel catfish and white bass were not sexually mature
at this time.‘
Water samples were taken the following day , on June 16, the analyses results
of which are given in Table 2.
On July 14, a c00perative investigation with the State Health Department was
made on Tierra Blanca Creek from Buffalo Lake westward to a point about 3 miles
west (upstream) from Hereford. The objective of this investigation was to locate
- sources of organic pollution. The locations of water sampling stations are shown
in Figure 2 and the results of water analyses are given in Table 3.
The major source of organic pollution is from cattle feed lots located on
the creek or on tributaries of the creek. Other sources contributing to the
organic loading of the creek were three vegetable-processing houses and one
slaughterhouse. ‘-
Summary:
Pollution from the Canyon sewage treatment plant killed fish in approximately
3_miles of Tierra Blanca Creek. Future pollution from this source could be
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Tabla 2. Analysis Results of'water Samples Taken from Buffalo Lake and
_ Tierra Blanca Creek, June 16, 1964. -.
Station 1 Station 2 Station 3 Station 4
.pH_ - 7.6
Conductivity, Micromhos I l ' 420
Total Dissolved Solids ppm 252
Chloride ppm _ _ 21
sulfates-ppm "I - _ l 25'
Chlorine Demand ppm ' I _ I '_ 3.5 ;
'Diaaolvad oxygen (field) ppm ' -4.0
-B.O.D..ppm- I - I ' 17‘
Ammonia Nitrogen-ppm 4.2
”Hitrita.Nitrogsn ppm I - 0.1-
Nitrata Nitrogen ppm I' 0.4-6
P. Alkalinity ppm 7 . O
".Tbta1 Alkalinity ppm - _ I'l44
I Floral Suspended Solids ppa' l I 447
'motal Volatila.8011da ppI! ' ' 68
'Total Fixed Solids.ppm .' -I_ '409
Station 1'- Upper End_Buffalo Lake in Polluted Area
Station 2 - Tierra Blanca Creek above Buffalo Lake
Station 3 - North Side Buffalo Lake
Station 4 - Buffalo Lake'Dam.
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prevented if the plant effluent was used for irrigation of nearby fields instead
of being released into the creek. Some of this effluent is now disposed of in this
manner, but sufficient amounts enter the creek to cause oxygen depletion during
periods of low water.
A serious threat to the fish p0pulation of Buffalo Lake exists in the accumulation
of organic materials in feed lots located in the Hereford area. Run-off from these
feed lots carries 6 tremendous organic load and results in a "slugging" of oxygen-
depleted water which destroys aquatic life downstream in Tierra Blanca Creek and the
upper end of Buffalo Lake. Other continuing sources of pollution are the Hereford
sewage treatment plant and the slaughterhouse, Seasonally, vegetable processing
houses contribute to the organic load.
'Recommendations:
This job should be continued. Special emphasis should be given to study of
feed lot pollution from the Hereford area, and to determining whether insecticides
are significant in any future fish kills that may occur from the same source.
I //:;/é/
Prepared by Lonnie Peters Approved by
Project co-leader . Coordinator
Leo D- Lewis
Date March 9, 1965
Regional Supervisor
JOB COMPLETION REPORT
State of - Texas
Project No. F-7-R-12 Name: -Fisheries Investigations and Surveys of the
Waters of Region l-A.
Job No. C-l Title: Pollution Studies gFisheries Region 1-A2)
Period Covered January 1, 1964 — December 31, 1964
Objectives:
- To determine the source and nature of natural or man~made pollutants which
affect fish pOpulations.
Procedure:
Fish kills or die-offs were investigated by field observations, counts of
fish killed, examinations of the fish, and chemical analysis of the affected
waters. Water analysis in the field included dissolved oxygen, carbon dioxide,
and pH determinations. Occasionally, water samples were sent to the State Health
Department laboratory in Austin for more detailed analysis. Searches above and
below affected areas were conducted in order to determine origin, type and extent
of pollution.
Findings:
Investigations were carried out at four lakes this year. One lake, Buffalo
Springs Lake in Lubbock County, is currently the subject of a study to determine
its limnological and game fish problems. Consequently, much information is
available on this lake, and information pertinent to pollutions problems is in-
cluded in this report.
The other three lakes were South Lake at Post, Reese Air Force Base Lake,
and McKenzie State Park Lake.
Buffalo Springs Lake
Buffalo Springs Lake is an end depository for almost all settleable solids
and many chemicals which originate in storm drains, dump grounds, feed lots, and
several industrial plants in Lubbock. Most probably, the majority of fish
mortalities at Buffalo Springs Lake are directly and/or indirectly the result
of the basic water quality which is produced on the watershed.“
_ Leuter's cattle feed lot constituted a source of pollutants that caused fish
kills in 1963. The feed lot effluent now drains into a retention pool. From .
the pool it is pumped into shallow, broad oxidation ponds and disposed of safely.
One of Lubbock's water reclamation plants is situated on the watershed.
Its effluent does not flow directly into Yellowhouse Canyon but is pumped into
large holding ponds and utilized for irrigation. The irrigated areas are drained
- into catchment tanks, but heavy rains and ground percolation provide eventual
transport of some of the materials from these waters into Buffalo Springs Lake.