TPWD 1969 F-18-R-4 #1284: Region I-D Fisheries Studies: Job No. 2 Pollution Studies, Federal Aid Project No. F-18-R-4
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JDB PRDGRESS REPDRT
As required by
FEDERAL AID IN FISHERIES RESTORATIDN ACT
TEXAS
Federal Aid Prujeet Nu. F-lS-R-h
REGIUN I-D FISHERIES STUDIES
Jab He. 2 Pullutiun Studies
Prujeet Leader: Geurge G. Sanderson, Jr.
Assistant Prujeet Leader: Runald R. Andersen
J. R. Singleten
Executive Direetur
Parks and Wildlife Department
Austin, Texas
Marian Teule Eugene A. Walker
D-J Cuerdinater Direetur, Wildliie Services
April 1?, 1969
SUMMARY
Six gravel washing cperaticns are cperating in Regicn I-D. Pclluticn bv
siltaticn cccurred en the Peccs River near Grandfalls and is cccurring near
Del Ric. Beth cperaticns are new being mcnitured by the Texas Water Quality
Beard and ccrrective acticn is being taken.
Dew Chemical Ccrpcraticu has established a flucrspar mine and mill en
the Ric Grande River at LaLinda. Prcject perscnnel visited the mill and tack
water samples in the Ric Grande. Analysis is iuccmplete.
A fish-kill occurred in July at the Balmcrhea State Park swimming peel and
at Lake Balmcrhea. The suspected causes are insecticides, heavy rain and asscc—
icated runcff, and drastic cxvgen level fluctuaticns due tc a heavy algae blccm.
An extensive fish—kill began in mid4chember 1968 en the Peccs River near
Sheffield and ccntinued intc December. Apprcximately ?0 miles cf river and
all species cf fish were affected. Suspected causes are salinitv, agricultural
chemicals and wastes, cil field pclluticn, and pussiblv unkncwn chemical acticn.
Draught and retenticn cf water by Red Bluff Lake have reduced water quantity
in the river and intensified the effect cf anv pcllutant.
A die—eff in Lake Imperial cccurred just befcre Christmas. We definite
date cr cause is kncwn. Pclluticu frcm cil field activities was cbserved in
the field in February. Geld weather cccurred just befcre the die-eff.
JflE PRUGRESS REPURT
State: Texas
Prcject Nc.: F-lS-R—A Same: Regicn 1—D Fisheries Studies
Jcb Nc.: 2 Title: Pclluticn Studies
Pericd Ccvered: March 1, 1968 thrcugh February 28, 1969
Objectives:
General:
Tc investigate instances cf pclluticn affecting specific fish pcpulaticns
and tc repcrt findings tn the State Water Quality Beard when remedial acticn
is needed.
Specific:
1, Tc determine extent cf damage tc fish pcpulaticns.
2. Tc trace the scurce cf pclluticn.
3. Tc determine the nature cf the pclluticn.
A. Tc delimit saline pclluticn and its effects en fish pcpulaticns in
the Peccs River belcw Red Bluff Lake and abcve the Ric Grande.
5. Tc repcrt instances cf viclaticn and negligence tc the State Water
Quality Ecard.
Prccedures:
General:
Pclluticn disccvered by prcject perscnnel cr repcrted tc prcject perscnnel
was investigated thrcugh cbservaticns, water analysis, fish pcpulaticn sampling,
and bicassay. The nature and scurce cf the pclluticn determined if remedial
measures were pcssible and needed. Saline pclluticn in the Peccs River was
extensively investigated by fishery survey, bicassay, and chemical analysis.
Specific:
1. Curscry cbservaticns cf sick cr dead fish were made tc establish
the length cf a stream cr area cf a lake affected. Pcpulaticn
sampling with nets andfcr seines were made tc establish number
and species cf fish surviving and were ccmpared with Fast samples
cr ”abcve and belcw” samples tc establish cverall changes in the
pcpulaticn ccmpcsiticn.
2. Frem the dcwnstream peint where dead fish were feund, a search was
made upstream fer evidence as te the seurce ef the pellutant. The
nature ef the pellutant (if knewn) might pinpeint the seurce.
Netted er seined fish were identified in the field where pessible. Names
ef fish used in this repert are these accepted by the American Fisheries Seciety
as published in their Special Publicatien He. 2, 1960, A List ef Cemmen and
Scientific Names ef Fishes Frem the United States and Canada, Secend Editien.
Standard survey gill nets are 150 feet leng when censtructed. The meshes
begin at 1-inch square and pregress te 3.5 inches square in 25—feet sectiens.
Large mesh nets are 150 feet leng when built and all mesh is 3.5 inches square.
The webbing cf all nets is 3 feet deep tied dewn te 6 feet. Sets are censtructed
as that they sink when set. The lead line fellews bettem centeurs and the fleats
suppert the webbing like a fence. Sets are usually made perpendicular re the
shereline in lakes and at an angle dcwnstream and acress in rivers.
Disselved exygen centent was checked in the field using a Kemmerer sampler
te extract samples and a Each kit te make the determinatiens. Salinity was
alse determined by bcth prcject persennel and the regienal chemist.
Findings:
Gravel Washing Cperatiens
There are A gravel washing eperatiens near Del Rie. Dne eperatien, en
Cienagas Creek, has allewed waste water te carry silt intc the creek and the
creek is cheked with silt fer censiderable distance belcw the eperatien.
Anether eperatien en Sycamere Creek is discharging waste water back intc the
creek. All these eperatiens are being menitered by Texas Water Quality Beard
field persennel.
Preject persennel examined a gravel washing eperatien en the Feces River
near Grandfalls, Texas, en May 22, 1968. Areas belcw, at, and abcve the epera-
tien were ebserved. Evidence cf pclluticn by siltatien was shcwn by increased
turbidity (6 inches secche) near the eperatien. Turbidity was 5 feet Secchi
abeut 300 yards upstream and abeut 1.5 miles dcwnstream frcm the eperatien.
The river was clegged with mud and silt fer apprcximately 150 yards at and
belcw the entrance cf the waste water (Figure l). The cenditiens were repcrted
te the Regienal Cffice and the eperatien is presently being menitered by the
Texas Water Quality Eeard field persennel. A large retentien pit has been
dug te retain wastes and new ne materials enter the river frem the eperatien.
There is a gravel washing eperatien just nerth ef U. S. 290 abeut 2 miles
east ef Sheffield in Peccs Ccunty. Waste water was being released inte an
arreye which jeined the Feces River. Texas Water Quality Beard field persennel
have visited the eperatien and cerrective actiens are underway.
GRA‘IEL WASHING WASTE WATER
Mining Uperatiens
The Dew Chemical Cempany has built a fluerspar mill at LaLinda, dewnriver
frem Bequillas Canyen en the Rie Grande River in Brewster Ceunty. The ere is
mined appreximately 15 miles seuth ef the mill in Mexice. Fluerspar extractien
frcm the ere is dene by crushing, pewdering, and:fletaticn. The dried preduct,
calcium flueride, is a gray talcum-like pewder. This pcwder is trucked acress
a bridge built by Dew te a railread terminal in the United States fer further
dispesal.
Water, eleic acid, quebrache, and sedium silicate are used in the fletatien
precess. A large dispesal pit permits settling cf mest ef the suspended selids.
During warm weather, evaperatien prevents waste water frcm entering the river.
During ceel weather, seme cf the excess water flews frem the pit inte the Ric
Grande. Water samples are periedically run by Dew chemists te meniter the
effluent. Preject persennel ebtained water samples abcve, at, and belcw the
mill te determine water quality. Analysis is incemplete.
The element beryllium was discevered in seme ef the fluerspar ere. Dew
persennel stated that all waste water frcm beryllium-centaining strata is being
placed in ether retaining structures until chemical tests indicate that the
material will net be bielegically harmful if it enters the Ric Crande.
Balmerhea Fish-Kill
A fish-kill at Lake Ealmerhea and in the springs at Salmerhea State Park
was repcrted en July 22, 1968 (Figure 2). The regienal chemist, the park super-
intendent, and prcject persennel met at the State Park and cenducted a study.
Suspected causes were: (A) Insecticide frcm an aerial applicatien te
cetten fields just west cf the State Park. The pilet was executing 1ew level
passes and turns. After ene typical lew pass, ene sprayer was still releasing
chemical during the turn and insecticide drifted inte the peel. The insecticide
mixture was 3 parts methyl parathien, 3 parts DDT, and 1 part texaphene.
(b) Heavy rains, tetaling 15 inches, eccurred in July. They intreduced
temperature changes and the springs were murky during the rains. This murky
cenditien is interpreted as caused by surface runeff inte the aquifer supplying
the spring. Crganic and chemical pellutants are theught te have entered the
springs by this means. The lake receives water frcm the springs and frcm
surface runeff.
(c) The sunfish pcpulaticn was spawning when the die—eff eccurred. During
spawning, fish are under stress and eften in a weakened cenditien. Sepyelegnie
infectiens eccur en weakened fish when scars are ebtained by fighting ever, er
pretecting, nesting sites and nests.
(d) Detritus carried by runeff entered the lake and caused exygen depletien.
The lewer strata in Lake Salmerhea were deveid ef exygen en July 23 and 24, 1968.
Asseciated cenditiens must have been present.
Figure 2
BALHORHEA FISHrKILL
(E) A heavy grewth ef algae was present in the springs en July 22. Super-
satured exygen cenditiens eccurred in seme areas ef the springs as a result ef
the algae grewth. The algae ceuld have been remeving practically all ef the
dissclved exygen frcm the water at night and en cleudy, calm days.
Discussien
The tests fer pesticides indicated DDT present in very small ameunts -
0.000A5 ppm maximum - in the water. Chrenic presence ef insecticides weuld
add a ccntinued stress facter which has net been demenstrated. Ne methyl
parathien er texaphene was present in the samples tested. Methyl parathien
detexifies very rapidly (Califernia Water Quality Criteria, publicatien Re.
3-A, states that the half-life en cetten leaves is less than ene beer). The
DDT present ceuld be standard fer the springs as nc prier calibratiens have
been made. DDT was present in very small ameunts — 0.053 ppm maximum — in the
fish flesh. This ameunt is censidered tee small tc acceunt fer the kill by
itself. He methyl parathien er texaphene was present in the fish flesh tested.
Methyl parathien disseciates very rapidly and its acticn in fish flesh is unknewn.
Cenclusiens
The abeve stress facters were acting en the fish pcpulaticn prier te the
die-eff. Weakened and fungus-infected fish might have begun dying regardless
ef the presence er absence ef insecticides. The timing ef deaths indicated
that pesticides were pessibly the everbalancing agent which accelerated the
deaths cf many fish. Fish began dying seen after winddrift depesited pesticides
in the spring in additien te that pessibly present in percelated water.
Tests sheuld be made te determine whether er net DDT is chrenically present
in the spring waters. Any change frem determined values weuld be apparent in
the event ef a future die-eff. The springs have a large velume ef flew. Much
ef the chemical intreduced by the spray plane weuld have been remeved by the
time tests were run. DDT is mentiened frequently and ceuld be used as an
indicater. DDT detexifies slewly and remains indefinitely in the water. If
DDT is net chrenically present in the spring water, the eccurrence ef DDT in
the chemical analysis is significant. Its presence weuld indicate that texaphene
and methyl parathien were alse present in ameunts cemparable te the spray
mixture, watershed use, percelated residues, and detexificatien time.
Synergistic acticn eften eccurs between chemicals which increases their
efficiency as insecticides (Califernia Water Quality Criteria, Ne. 3A, page
26}. The effect ef mixed DDT, texaphene, and methyl parathien en fish is
unknewn. Synergistic actien, if present, ef methyl parathien, texaphene, and
DDT in very small ameunts ceuld have been the everbalancing facter in many
deaths.
Feces River Fish-Kill
An extensive fish—kill began in mid—Nevember 1968, en the Feces River
near Sheffield and ccntinued inte December. Apparently all species present
were affected (Figure 3}. The kill extended frem abeut 5 miles belcw U. S.
6? te belcw lndependence Creek {Figure A).
Figure 3
PECOS RISER FISHFKTLL EAST OF SHEFFIELD
E5 mterstsfe Highway
'“' H s H‘ 1
Iii . . ”WHEY
EB State Highway
FEET-“arm er Ranch Fear]
It: Avri c'Il feral Area
4!" Area Dead Fish Fever? and Fish Tiffanied
if" Area Practically He'reid ef Fish
3"? Extent. ef' Invesljgatlen
P Pig Pen
Pew-F Hen-1:15
Figure A