U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
LIVINGSTON RESERVOIR
POLK, SAN JACIMTO, TRINITY,
AND WLKER COUNTIES
TEXAS
EPA REGION VI
WORKING PAPER No, 651
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
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REPORT
ON
LIVINGSTON RESERVOIR
POLK, SAN JACWO, TRINITY,
AND WALKER COUNTIES
TEXAS
EPA REGION VI
WORKING PAPER No, 651
WITH THE COOPERATION OF THE
TEXAS WATER QUALITY BOARD
AND THE
TEXAS NATIONAL GUARD
FEBRUARY/ 1977
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CONTENTS
Page
Foreward • i i
List of Texas Study Reservoirs iv
Lake and Drainage Area Map vi
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 12
V. Literature Reviewed 18
VI. Appendices 19
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11
FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to freshwater lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:
a. A generalized representation or model relating
sources, concentrations, and impacts can be constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized model
can be transformed into an operational representation of
a lake, its drainage basin, and related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented. The report is formatted to provide state environmental
agencies with specific Information for basin planning [§303(e)j, water
quality criteria/standards review [§303(c)], clean lakes [§314(a,bj],
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
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Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condi-
tion are being made to advance the rationale and data base for
refinement of nutrient water quality criteria for the Nation's
fresh water lakes. Likewise, multivariate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
in the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.
ACKNOWLEDGEMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Texas Water Quality Board
for professional involvement, to the Texas National Guard for
conducting the tributary sampling phase of the Survey, and to
those Texas wastewater treatment plant operators who voluntarily
provided effluent samples.
Hugh C. Yantis, Jr., Executive Director of the Texas Water
Quality Board, and John B. Latchford, Jr., Director, and the staff
of the Field Operations Division provided invaluable lake documen-
tation and counsel during the Survey, reviewed the preliminary
reports, and provided critiques most useful in the preparation of
this Working Paper series.
Major General Thomas Bishop, the Adjutant General of Texas,
and Project Officer Colonel William L. Seals, who directed the
volunteer efforts of the Texas National Guardsmen, are also grate-
fully acknowledged for their assistance to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY RESERVOIRS
State of Texas
NAME
Amistad
Bastrop
Bel ton
Braunig
Brownwood
Buchanan
Caddo
•
Calaveras
Canyon
Colorado City
Corpus Christi
Diversion
Eagle Mountain
Fort Phantom Hill
Houston
Kemp
Lake O'The Pines
Lavon
Lewisville (Garza-Little Elm)
Livingston
COUNTY
Val Verde
Bastrop
Bell, Coryell
Bexar
Brown
Burnet, Llano
Harrison, Marion, TX;
Caddo Parish, LA
Bexar
Comal
Mitchell
Jim Wells, Live Oak, San
Patricio
Archer, Baylor
Tarrant, Wise
Jones
Harris
Baylor
Camp, Marion, Morris,
Upshur
Coll in
Denton
Polk, San Jacinto, Trinity,
Walker
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Lyndon B. Johnson
Medi na
Meredith
0. C. Fisher (San Angelo)
Palestine
Possum Kingdom
Sam Rayburn
Somerville
E. V. Spence
Stamford
Still house Hollow
Tawakoni
Texoma
Travis
Trinidad
Twin Buttes
White River
Whitney
Wright Patman (Texarkana)
Burnet, Llano
Bandera, Medina
Hutchinson, Moore,
Potter
Tom Green
Anderson, Cherokee,
Henderson, Smith
Palo Pinto, Stephens,
Young
Angelina, Jasper
Nacogdoches, Sabine, San
Augustine
Burleson, Lee, Washington
Coke
Haskell
Bell
Hunt, Rains, Van Zandt
Cooke, Grayson TX; Bryan,
Johnston, Love, Marshall, OK
Burnet, Travis
Henderson
Tom Green
Crosby
Bosque, Hill
Bowie, Cass
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jroo'—I
I I
h
\
Palestine
LIVINGSTON RESERVOIR
® Tributary Sampling Site
X Lake Sampling Site
Jl Sewage Treatment Facility
to 20 Mi.
Scale
i-
Map Location
V
V vY:/,
^--
LIVINGSTON
RESERVOIR
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LIVINGSTON RESERVOIR
STORE! NO. 4820
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Livingston Reservoir is eutrophic;
i.e., well supplied with nutrients and quite productive. Whether
nutrient enrichment is beneficial or deleterious depends on the
actual or potential effect on the uses of the reservoir. In this
regard, the Texas Water Quality Board has indicated that there is
little or no known impairment of the designated beneficial uses
of this water body.
Livingston Reservoir ranked last in overall trophic quality
when the 39 Texas reservoirs sampled in 1974 were compared using
a combination of six water quality parameters*. Thirty-seven of
the reservoirs had less median total phosphorus, median dissolved
orthophosphorus, and median inorganic nitrogen; 28 had less mean
chlorophyll a_, and 23 had greater mean Secchi disc transparency.
Marked depression or depletion of dissolved oxygen with depth
occurred at all stations in May and August.
Survey limnologists noted emergent vegetation in March at sta-
tions 6 and 8; in May at stations 2, 5, 7, and 8; and in August at
station 2. In another study on this water body, macrophyte growths
sufficient to impede boat traffic in several areas were reported
(Anonymous, 1974 [?]).
* See Appendix A.
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B. Rate-Limiting Nutrient:
The algal assay results indicate that Livingston Reservoir
was limited by nitrogen at the times samples were collected
(03/16/74 and 11/17/74). The reservoir data indicate nitrogen
limitation at all sampling stations and times. Other investi-
gators also have indicated that the reservoir is nutrient-enriched
and limited by nitrogen (Huang, Mase, and Fruh, 1973).
C. Nutrient Controllability:
1. Point sources—During the sampling year, listed point
sources contributed 2.0% of the total phosphorus load to Livingston
Reservoir. The wastewater treatment plant at Huntsville was the
largest contributor of 14 municipal facilities and accounted for
1.1% of the total.
The present phosphorus loading of 6.43 g/m2/year is eight
times that proposed by Vollenweider (Vollenweider and Dillon,
1974) as a eutrophic loading (see page 17). Even complete removal
of phosphorus at the listed point sources would not significantly
decrease the present loading, although phosphorus removal at
Huntsville could result in some improvement in Harmon Creek
embayment; a major portion of the load in this tributary appears
to be from the wastewater treatment plant as indicated by high
nutrient concentrations at station. E-l (see Appendix E). However,
overall improvement in trophic quality is dependent upon the con-
trollability of phosphorus from upstream sources which impact the
Trinity River (see discussion below).
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2. Non-point sources—During the sampling year, non-point
sources contributed 98.0% of the total phosphorus input to
Livingston Reservoir. The Trinity River contributed 97.3% of this
total, four other gaged tributaries contributed less than 0.1%,
and the ungaged minor tributaries and immediate drainage contributed
an estimated 0.4%.
The non-point phosphorus export rate of the Trinity River (52
kg/km2/year) is over 15 times the mean of the exports of the other
gaged tributaries of Livingston.Reservoir (see page 16) and is
indicative of additional point sources upstream; e.g., the Dallas
metropolitan area. Further investigation is needed to determine
the controllability of phosphorus from all point sources as well as
from land-use practices in the Trinity River drainage basin.
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LI. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphometry :
1. Surface area: 334.28 kilometers2.
2. Mean depth: 6.5 meters.
3. Maximum depth: >21.3 meters.
4. Volume: 2,158.608 x 106 m3.
5. Mean hydraulic retention time: 130 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Trinity River 39,943.0 173.930
Palmetto Creek 52.3 0.188
E. Carolina Creek 31.6 0.118
Mammon Creek 114.0 0.500
Rocky Creek 100.8 0.460
Minor tributaries &
immediate drainage - 2,374.0 16.380
Totals 42,615.7 191.576
2. Outlet -
Trinity River 42,950.0** 191.550
C. Precipitation***:
1. Year of sampling: 144.8 centimeters.
2. Mean annual: 114.3 centimeters.
t Table of metric conversions—Appendix B.
tt Anonymous, 1974(7).
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of reservoir.
*** See Working Paper No. 175.
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III. WATER QUALITY SUMMARY
Livingston Reservoir was sampled four times in 1974 by means of a
pontoon-equipped Huey helicopter. Each time, samples for physical and
chemical parameters were collected from two or more depths at eight
stations on the reservoir (see map, page vi). During each visit, a
single depth-integrated (4.6 m to surface) sample was composited from
the stations for phytoplankton identification and enumeration; and
during the March and November visits, 18.9-liter depth-integrated
samples were composited from stations 1, 2, 3, and 4 and 5, 6, 7, and
8 for algal assays. Also each time, a depth-integrated sample was
collected from each of the stations for chlorophyll £ analysis. The
maximum depths sampled were 21.3 meters at station 1, 19.5 meters at
station 2, 15.8 meters at station 3, 7.6 meters at station 4, 17.1
meters at station 5, 15.5 meters at station 6, 11.9 meters at station
7, and 12.5 meters at station 8.
The sampling results are presented in full in Appendix D and are
summarized in the following table (the August nutrient samples were
not properly preserved and were not analyzed).
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PARAMETER
TEMP (C)
OISS OXY (MG/L)
CNDCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (MG/L)
N02»N03 (MG/L)
AMMONIA (MG/L)
KJEL N (MG/L)
IMORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/L)
SECCHI (METERS)
' A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 3/16/74)
& SITES
RANGE MEAN MEDIAN
14.3 - 19.7 18.3 18.7
2.8 - 9.0 7.0 7.9
211. - 447. 299. 281.
6.8 - 8.3 7.5 7.6
55. - 112. 81. 77.
0.150 - 0.588 0.280 0.229
0.086 - 0.470 0.202 0.150
0.370 - 1.520 0.794 0.660
0.040 - 0.280 0.082 0.060
0.500 - 1.100 0.806 0.800
0.410 - 1.720 0.876 0.725
1.120 - 2.590 1.599 1.435
6.0 - 46.3 19.
0.5 - 1.0 0.7 0.8
CHEMICAL CHAWACT£*ISTICS FO* LIVINSSTON LAKE
STORET CODE 4«20
2ND SAMPLING ( 5/24/74)
a SITES
RANGE
21.3 - 29.6
0.4 - 12.8
276. - 463.
7.3 - 9.5
80. - 111.
0.097 - 0.267
0.036 - 0.215
0.060 - 1.150
0.040 - 0.390
0.500 - 1.900
0.100 - 1.210
0.580 - 2.010
2.3 - 42.9
0.6 - 1.5
MEAN
26.7
4.4
392.
8.2
97.
0.186
0.123
0.404
0.093
0.795
0.497
1.199
10.6
1.0
MEDIAN
26.7
4.1
402.
7.9
97.
0.185
0.117
0.270
0.070
0.700
0.375
1.120
6.2
1.0
3*0 SAMPLING ( 8/19/74)
8 SITES
RANGE MEAN MEDIAN
26.0 - 31.7 39.1 29.0
0.0 - 10.4 3.2 1.0
406. - 720. 485. 458.
7.3 - 9.2 8.0 7.9
oooooo -oooooooooooooooooooooo
oooooo -oooooooooooooooooooooo
oeooo* -oooooooooooooooooooooo
OO«OOO -OOOOOOOOOOOOOOOOOOOOOO
oooooo -o«o
oooooo -oooooooooooooooooooooo
oooooo -ootto«ooo»ooo»«»»oo»ooo
-OOOOOOOOOOOOOOOOvOOOOO
19.7 - 28.0 24.1 24.5
0.9 - 1.6 1.2 1.1
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A. SUMMARY Of PHYSICAL AND CHEMICAL C^A^ACTtfilSTiCS r~0~< LIVINGSTON LAKE
STCWET COOE <*«20
4TH SAMPLING (ll/ 6/74)
PARAMETER
TEMP (C)
OISS OXY (MG/L)
CNOCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MO/LI
TOT P (MG/L)
ORTHO P (MG/L)
N02*N03 (MG/L)
AMMONIA (MG/L)
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/D
5ECCHI (METERS)
RANGE
19.2 - 23.0
4.0 - 7.8
18^. - 339.
7.0 - 7.9
51. - 96.
0.113 - 0.760
0.076 - 0.397
0.230 - 1.350
0.020 - 0.220
0.400 - 1.200
0.250 - 1.410
0.730 - 2.050
2.8 - 15.8
0.2 - 1.4
8 SITES
MEAN MEDIAN
21.0
6.2
263.
7.4
79.
0.278
0.173
0.481
0.048
0.703
0.530
1.184
10.3
0.6
20.7
5.8
26U.
7.4
82.
0.214
0.128
0.350
0.035
Oi700
0.390
1.055
12.5
0.5
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8
B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
03/16/74
05/24/74
08/19/74
11/06-07/74
Dominant
Genera
1. Cyclotella sp.
2. Melosira "sp.
3. Stephanodiscus sp.
4. Chroomonas sp.
5. Synedra sp.
Other genera
Total
1. Centric diatoms
2. Merismopedia sp.
3. Carteria sp.
4. Chroomonas sp.
5. MelosiraTp.
Other genera
Total
1. Dactylococcopsis sp.
2. Cyclotella sp.
3. Merismopedia s£.
4. Oscillatoria SJD.
5. Raphidiopsis S£.
Other genera
Total
1. Stephanodiscus sp.
2. Melosira sp.
3. Cryptomonas sp.
4. OscillatoTTa sp.
5. Dactylococcopsis sp.
Other genera
Total
Algal Units
per ml
5,017
9,488
9,
1
691
068
"916
687
686
2,443
15,491
7,832
6,633
6,562
5,151
3,669
2,752
32,599
1,097
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2. Chlorophyll a^
Sampling Station Chlorophyll a_
Date Number (pg/1)
03/16/74 1 24.9
2 46.3
3 27.6
4 19.0
5 7.3
6 12.2
7 6.0
8 12.1
05/24/74 1 5.0
2 5.2
3 6.7
4 2.3
5 5.7
6 42.9
7 6.9
8. 10.4
08/19/74 1 19.7
2 22.3
3 28.0
4 23.6
5 21.3
6 26.1
7 25.4
& 26.1
11/06-07/74 1 12.9
2 15.8
3 14.0
4 12.2
5 7.1
6 2.8
7 14.4
8 3.4
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10
C. Limiting Nutrient Study:
. 1. Autoclaved, filtered, and nutrient spiked -
a. March sample -
(1). Stations 1, 2, 3, and 4.
Spike (mg/1)
Ortho P
Cone, (mg/1)
Inorganic N
Cone, (mg/1)
Control
0.050 P
0.050 P + 1.0
1.0 N
0.125
0.175
N 0.175
0.125
(2). Stations 5, 6, 7, and
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0
1.0 N
b. November
Ortho P
Cone, (mg/1)
0.295
0.345
N 0.345
0.295
sample -
(1). Stations 1, 2, 3, and
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0
1.0 N
Ortho P
Cone, (mg/1)
0.096
0.146
N 0.146
0.096
(2). Stations 5, 6, 7, and
Spike (mg/1)
Control
0.050 P
0.050 P-+ 1.0
1.0 N
Ortho P
Cone, (mg/1)
0.246
0.296
N 0.296
0.246
0.720
0.720
1.720
1.720
8.
Inorganic N
Cone, (mg/1)
1.014
1.014
2.014
2.014
4.
Inorganic N
. Cone, (mg/1 )
0.273
0.273
1.273
1.273
8.
Inorganic N
Cone, (mg/1)
0.690
0.690
1.690
1.690
Maximum yield
(mg/1-dry wt.l
15.4
15.1
31.1
34.7
Maximum yield
(mg/1-dry wt.)
23.0
23.6
41.5
37.3
Maximum yield
(mg/1-dry wt.)
1.2
1.5
5.5
3.2
Maximum yield
(mg/1-dry wt.)
23.0
24.0
55.8
53.9
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11
3. Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate that the potential primary productivity
of Livingston Reservoir was moderately high to very high
at the times the samples were collected. Also, in all
assays the lack of response with the addition of phosphorus
until nitrogen was added, indicates that the reservoir was
limited by nitrogen at those times. Note that the addition
of only nitrogen resulted in yields which were significantly
greater than those of the controls.
The reservoir data also indicate nitrogen limitation;
i.e., the mean inorganic nitrogen/orthophosphorus ratios
ranged from 13/1 at station 1 in March to 2/1 at station 8
in November, and nitrogen limitation would be expected.
Nitrogen limitation, as indicated by the algal assay or
by in-lake nitrogen to phosphorus ratios, does not necessarily
mean that the trophic condition of the reservoir can be im-
proved by controlling nitrogen inputs. In many cases, the
apparent condition of nitrogen-limitation results from excessive
phosphorus input from point sources and is often accompanied
by a corresponding increase in primary production. In such
cases, the reversal of the enriched condition depends upon
phosphorus control, not nitrogen control.
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12
IV." NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of .nutrient loadings, the Texas National
Guard collected monthly near-surface grab samples from each of the
tributary sites indicated on the map (page vi), except for the month
of April when two samples were collected. Sampling was begun in
September, 1974, and was completed in August, 1975.
Through an interagency agreement, stream flow estimates for the
year of sampling and a "normalized" or average year were provided by
the Texas District Office of the U.S. Geological Survey for the
tributary sites nearest the reservoir.
In this report, nutrient loads for sampled tributaries were
determined by using a modification of a U.S. Geological Survey computer
program for calculating stream loadings*. Nutrient loads shown are
those measured minus point-source loads, if any. However, the nutrient
loads estimated for the Huntsville wastewater treatment plant exceeded
the loads measured in Harmon Creek at station E-l, and the background
loads for this tributary and the unsampled "minor tributaries and imme-
diate drainage" ("II" of U.S.G.S.) were estimated using the means of the
nutrient loads, in kg/km2/yr, at stations B-l, C-l, and H-l and multi-
plying the means by E-l and ZZ areas in km2.
The operators of the Galloways Marina, Madisonville, Memorial Point,
Normangee, Texas Department of Corrections, and Trinity wastewater treat-
ment plants provided monthly effluent samples and corresponding flow data.
* See Working Paper No. 175.
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13
The operators of eight other listed wastewater facilities did not par-
ticipate; nutrient loads from these sources were estimated at 1.134 kg P
and 3.401 kg N/capita/year, and flows were estimated at 0.3785 m3/capita/
day.
A. Waste Sources:
1. Known municipal* -
Pop.
Name Served
Centerville** 600
Crockett**
Plant #1 5,800
Plant #2 1,200 •
Galloways Marina 200
Treatment
stab, pond
tr. filter,
act. sludge
act. sludge
act. sludge
Mean Flow
(m3/d)
227.1
2,195.3
454.2
3.9
(campground)
Groveton** 700
Huntsville 20,000
Kalita Point 20
Lovelady 388
Madisonville 3,050
Memorial Point 300
Normangee 670
TX Dept. of Cor 2,00
Imhoff tank
tr. filter
tertiary
ext. aer.
act. sludge
act. sludge
stab, pond
Imhoff tank
265.0
7,570.0
7.6
146.9
854.9
226.1
110.8
763.5
Receiving
Water
Little Beaver
Creek
Gail Creek
Tantabogue
Creek
White Rock
Creek
Kickapoo Creek
Town Branch
Lake Livingston
Tantabogue ^ree
Caney Creek'
Lake Livingston
Hollis Creek
Turkey Creek
rections
Trinity 3,000
2. Industrial - Unknown
act. sludge
678.6
Lake Livingston
* Treatment plant questionnaires.
** Anonymous, 1971.
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14
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Trinity River 2,091,430 97.3
Palmetto Creek 200 <0.1
E. Carolina Creek 90 <0.1
Harmon Creek 380 <0.1
Rocky Creek 405 <0.1
b. Minor tributaries & immediate
drainage (non-point load) - 7,935 0.4
c. Known municipal STP's -
Centerville 680 <0.1
Crockett 7,940 0.4
Galloways Marina 10 <0.1
Groveton 795 <0.1
Huntsville 22,680 1.1
Kalita Point 25 <0.1
Lovelady 440 <0.1
Madisonville 6,300 0.3
Memorial Point 70 <0.1
Normangee 110 <0.1
TX Dept. of Corrections 1,700 0.1
Trinity 1,490 0.1
d. Septic tanks* - 30 <0.1
e. Industrial - Unknown ?
f. Direct precipitation** - 5,850 _0_.3
Total 2,148,560 100.0
2. Outputs -
Lake outlet - Trinity River 923,050
3. Net annual P accumulation - 1,225,510 kg.
* Estimate based on 104 lakeshore dwellings; see Norking Paper No. 175.
** See Working Paper No. 175.
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15
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Trinity River 11,648,965 94.1
Palmetto Creek 4,695 <0.1
E. Carolina Creek 2,985 <0.1
Harmon Creek 10,220 0.1
Rocky Creek 11,450 0.1
b. Minor tributaries & immediate
drainage (non-point load) - 212,870 1.7
c. Known municipal STP's -
Centerville 2,040 <0.1
Crockett 23,805 0.2
Galloways Marina 80 <0.1
Groveton 2,380 <0.1
Huntsville 68,020 0.6
Kalita Point 70 <0.1
Lovelady 1,320 <0.1
Madisonville 11,285 0.1
Memorial Point 215 <0.1
Normangee 325 <0.1
TX Dept. of Corrections 3,930 <0.1
Trinity 4,990 <0.1
d. Septic tanks* - 1,110 <0.1
e. Industrial - Unknown ?
f. Direct precipitation** - 360,890 2.9
Total 12,371,645 100.0
2. Outputs -
Lake outlet - Trinity River 7,703,650
3. Net annual N accumulation - 4,667,995 kg.
* Estimate based on 104 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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16
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Trinity River 52 292
Palmetto Creek 4 90
E. Carolina Creek 3 94
Rocky Creek 3 85
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
W. Carolina Creek 0.067 0.911
Chalk Creek 0.026 0.715
Kickapoo Creek 0.094 0.896
-------
17
F. Yearly Loads:
In the following table, the existing phosphorus loadings
are compared to those proposed by Vollenweider (Vollenweider
and Dillon, 1974). Essentially, his "dangerous" loading is
one at which the receiving water would become eutrophic or
remain eutrophic; his "permissible" loading is that which
would result in the receiving water remaining oligotrophic
or becoming oligotrophic if morphometry permitted. A meso-
trophic loading would be considered one between "dangerous"
and "permissible".
Note that Vollenweider's model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/mVyr 6.43 3.67 37.0 14.0
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Livingston Reservoir:
"Dangerous" (eutrophic loading) 0.80
"Permissible" (oligotrophic loading) 0.40
-------
18
V. LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. EPA Publ
OWP-1, vol 6, Wash., DC.
Anonymous, 1974(7). Intensive surface water monitoring survey for
segment 0803 (Lake Livingston). Rept. No. IMS 9. TX Water Qual
Bd., Austin.
Huang, Vikki H., J. Rusty Mase, and E. Gus Fruh, 1973. Nutrient
studies in Texas impoundments. Jour. Water Poll. Contr. Fed.,
vol. 45, no. 1 (Jan.), pp. 105-118.
Vollenweider, R. A., and P. J. Dillon, 1974. The application^ of
the phosphorus loading concept to eutrophication research'.
Natl. Res. Council of Canada Publ. No. 13690, Canada Centre
for Inland Waters, Burlington, Ontario.
-------
19
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
-------
LAKES RANGED OY INDE.X N'lS,
RANK LAKE CODE LAKE NAME
INDEX NO
i 4809 CANYON RESERVOIR 445
2 4823 LAKE MEREDITH a41
3 4813- EAGLE MOUNTAIN LAKE 430
4 4816 KEMP LAKE 423
5 4801 AMISTAO LAKE 402
6 4805 SROwNWOOD LAKE 394
7 480? BASTROP LAKE 393
8 4838 WHITE RIVER RESERVOIR 390
9 4825 POSSUM KINGDOM RESERVOIR 387
10 4835 TRAVIS LAKE 384
11 4803 BELTON RESERVOIR 384
12 4831 STILLHOUSE HOLLOW RESERV 372
13 4812 DIVERSION LAKE 372
14 4808 CALAVERAS LAKE 362
15 4839 WHITNEY LAKE 357
16 4822 MEDINA LAKE 342
17 4827 SAM RAYBURN RESERVOIR 322
18 4828 E V SPENCE RESERVOIR 321
19 4837 TWIN 8UTTES RESERVOIR 311
20 4810 LAKE COLORADO CITY 310
21 4824 PALESTINE LAKE 302
22 4818 LAKE OF THE PINES 298
23 4807 CADOO LAKE 297
24 4814 FT PHANTOM HILL LAKE 296
25 4806 LAKE BUCHANAN 261
26 4830 STAMFORD LAKE 259
27 4819 LAVON RESERVOIR 258
28 4832 TAWAKONI LAKE 253
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
29 4821 LYNDON B JOHNSON LAKE 238
30 4834 TEXOMA LAKE 217
31 4829 SOMERVILLE LAKE 208
32 4826 SAN ANGELO HESERVOIR 200
33 4833 TEXARKANA LAKE 176
34 4815 GARZA LITTLE ELM RESERvO 173
35 4836 TRINIDAD 169
36 4804 BRAUNIG LAKE 159
37 4811 CORPUS CRIST I LAKE 155
38 4817 HOUSTON LAKE 139
39 4820 LIVINGSTON LAKE 91
-------
DfcTA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
4601 AMISTAD LAKE
4802 8ASTROP LAKE
4803 8ELTON RESERVOIR
4804 BRAUNIG LAKE
4805 BROWNWOOD LAKE
4806 LAKE 8IICHANAN
4807 CAODO LAKE
4808 CALAVERAS LAKE
4809 CANYON RESERVOIR
4810 LAKE COLORADO CITY
4811 CORPUS CRISTI LAKE
4812 DIVERSION LAKE
4813 EAGLE MOUNTAIN LAKE
4814 FT PHANTOM HILL LAKE
4815 GARZA LITTLE ELM RESEHVO
4816 KEMP LAKE
4817 HOUSTON LAKE
4818 LAKE OF THE PINES
4819 LAVON RESERVOIR
4630 LIVINGSTON LAKE
4821 LYNDON 8 JOHNSON LAKE
4822 MEDINA LAKE
4823 LAKE MEREDITH
4824 PALESTINE LAKE
4825 POSSUM KINGDOM RESERVOIR
4826 SAN ANGELO RESERVOIR
4827 SAM RAvBURN RESERVOIR
4828 E V SPENCE RESERVOIR
MEDIAN
TOTAL P
0.013
0.02?
0.016
0.134
0.027
0.036
0.055
0.038
0.010
0.042
0.113
0.025
0.024
0.060
0.045
0.023
0.097
0.031
0.063
0.196
0.042
0.010
0.021
0.031
0.023
0*093
0.029
0.036
MEDIAN
INO^G N
0.500
0.090
0.165
0.150
0.100
0.250
0.070
0.060
0.450
0.090
0.130
0.080
0.070
0.105
0.380
0.110
0.260
0.090
0.180
0.555
0.420
0.600
0.070
0.180
0.070
0.140
0.150
0.080
500-
MEAN SEC
371.474
419.917
378.312
461.625
470.375
437.625
463.333
461.667
384.812
473.625
475.187
470.111
469.625
474.909
475.782
455.000
486.187
440.000
485.333
465.469
456.500
403.562
439.312
442.625
419.045
481.000
439.458
462.583
MEAN
CHLOKA
2.042
12.392
8.025
22.762
4.887
8.606
14.808
22.500
2.500
12.675
19.756
15.867
5.662
6.317
14.156
10.217
16.650
12.919
5.400
16.112
8.100
12.944
3.037
10.619
9.495
24.675
6.267
11.775
15-
MIN 00
14.900
15.000
IS. 000
14.800
14.400
15.000
11.400
13.000
14.800
10.200
14.000
9.000
11.000
9.000
14.600
10.400
12.400
15.000
8.800
15.000
14.900
15.000
14.900
14.800
15.000
10.200
15.000
15.000
MEDIAN
DISS OrfTriO P
0.009
0..007
0.007
0.062
0.007
0.012
0.013
0.007
0.006
0.012
0.050
0.009
0.008
0.022
0.018
0.007
0.036
0.011
0.018
0.128
0.013
0.004
0.009
0.010
0.009
0.011
0.009
0.008
-------
LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
4829 SOMERVILLE LAKE
4830 STAMFORD LAKE
4831 STILLHOUSE HOLLOW RESEKV
4832 TAWAKONI LAKE
4833 TEXARKANA LAKE
4834 TEXOMA LAKE
4835 TRAVIS LAKE
4836 TRINIDAD
4837 TWIN BUTTES RESERVOIR
4838 WHITE RIVER RESERVOIR
4839 WHITNEY LAKE
MEDIAN
TOTAL P
0.053
0.073
0.018
0.046
0.106
0.042
0.018
0.389
0.029
0.020
0.028
MEDIAN
iNOrtG N
0.115
O.C60
0.160
0.100
0.120
0.160
0.250
O.liO
0.250
0.110
0.120
500-
MEAN SEC
473.833
482.714
406.250
466.417
475.500
451.321
389.913
479.500
454.917
434.500
430.500
MEAN
CHLOPA
24.^*91
18.457
3.917
16.246
19.119
12.493
5.595
24.300
8.708
4.333
6.912
Ib-
MlN DO
13.000
10.600
15.000
13.200
12.400
15.000
15.000
10.000
14.800
15.000
15.000
MEDIAN
DISS CMTHO
0.013
0.012
0.010
0.013
0.030
0.018
0.007
0.240
0.009
0.009
0.008
-------
OF LAKES airn HIGHER VALUES (NUMBED OF L
LAKE
CODE LAKE NAME
4801 AMISTAO LAKE
4802 HASTROP LAKE
4803 8ELTON RESEKVOIR
4804 BRAUNIG LAKE
4805 8ROWNWOOO LAKE
4806 LAKE BUCHANAN
4807 CADOO LAKE
4808 CALAVERAS LAKE
4609 CANYON RESERVOIR
4810 LAKE COLORADO CITY
4811 CORPUS CRISTI LAKE
4812 DIVERSION LAKE
4813 EAGLE MOUNTAIN LAKE
4814 FT PHANTOM HILL LAKE
4815 GARZA LITTLE ELM RESERVO
4816 KEMP LAKE
4817 HOUSTON LAKE
4818 LAKE OF THE PINES
4819 LAVON RESERVOIR
4820 LIVINGSTON LAKE
4821 LYNDON 8 JOHNSON LAKE
4822 MEDINA LAKE
4823 LAKE MEREDITH
4824 PALESTINE LAKE
4825 POSSUM KINGDOM RESERVOIR
4826 SAN ANGELO RESERVOIR
4827 SAM RAYBURN RESERVOIR
4828 E V SPENCE RESERVOIR
i7ri HiGhtK VALUES!
MEDIAN
TOTAL P
95
79
92
5
66
47
26
45
99
39
8
68
71
24
34
76
16
54
21
3
39
99
82
54
74
13
59
50
( 36)
( 30)
( 35)
( 2)
( 25)
< 18)
( 10)
( 17)
( 37)
( 14)
( 3)
( 26>
( 27)
< 9)
( 13)
( 29)
( 6)
( 20)
( 8)
( 1)
( 14)
( 37)
( 31)
( 20)
( 28)
( 5)
( 22)
( 19)
MEDIAN
IN03G N
5
76
26
42
70
21
91
100
8
76
47
83
91
66
13
61
16
76
29
3
11
0
91
32
91
45
39
83
( 2)
( 28)
( 10)
( 16)
( 26)
( 7)
( 33)
( 38)
( 3)
( 28)
( 18)
( 31)
( 33)
( 25)
( 5)
( 22)
( 6)
( 28)
( ID
( 1)
( 4)
( 0)
( 33)
( 12)
< 33)
( 17)
( 15)
( 31)
500-
MEAN SEC
100
a2
97
50
29
74
42
47
95
26
18
32
34
21
16
55
0
66
3
39
53
89
71
63
84
8
68
45
( 36)
( 3D
( 37)
( 19)
( ID
( 28)
( 16)
( 18)
( 36)
( 10)
( 7)
( 12)
< 13)
( 8)
( 6)
( 21)
( 01
( 25)
( D
( 15)
( 20)
( 34)
( 27)
( 24)
( 32)
( 3)
( 26)
( 17)
MEAN
CrtLOrtA
100
-47
68
8
87
63
32
11
97
42
13
29
79
74
34
55
24
39
84
26
66
37
95
53
58
0
76
50
( 38)
( 18)
( 26)
( 3)
( 33)
( 24)
( 12)
( 4)
( 37)
( 16)
( 5)
( ID
( 30)
( 28)
( 13)
( 2D
( 9)
( 15)
( 32)
( 10)
( 25)
( 14)
( 36)
( 20)
( 22)
( 0)
( 29)
( 19)
15-
MIN DO
39
17
17
49
58
17
76
67
49
88
61
97
79
95
55
84
72
17
100
17
39
17
39
49
17
88
17
17
( 14)
( 0)
( 0)
( 17)
( 22)
( 0)
( 29)
< 25)
< 17)
f 33)
( 23)
( 37)
( 30)
( 36)
( 21)
( 32)
( 27)
( 0)
( 38)
< 0)
( 14)
( 0)
( 14)
( 17)
( 0)
( 33)
( 0)
( 0)
MEDIAN
OISS OnThO P
63
92
84
5
84
39
30
92
97
39
a
63
76
16
21
92
11
46
21
3
30
100
63
51
63
46
63
76
( 21)
( 34)
( 3D
( 2)
( 3D
( 14)
( 10)
( 34)
( 37)
( 14)
( 3)
( 21)
( 28)
( 6)
( 7)
( 34)
( 4)
( 17)
< 7)
( 1)
( 10)
( 36)
( 21)
( 19)
( 21)
( 17)
I 21)
( 28)
INDEX
NO
402
393
364
159
394
261
297
362
445
310
155
372
430
296
173
423
139
298
258
91
238
342
441
302
387
200
322
321
-------
PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES *ITH HIGHER VALUES)
LAKE
CODE LAKE NAME
4829 SOMERVILLE. LAKE
4830 STAMFORD LAKE
4831 STILLHOUSE HOLLOW
4832 TAWAKONI LAKE
4833 TEAARKANA LAKE
4834 TEXOMA LAKE
4835 TRAVIS LAKE
4836 THINIOAO
4837 TWIN 8UTTES RESERVOIR
4838 WHITE RIVER RESERVOIR
4839 WHITNEY LAKE
MEDIAN
TOTAL P
2*
18
88
32
11
39
88
0
59
84
63
( 11)
( 7)
( 33)
( 12)
( 4)
( 14)
( 33)
( 0)
< 22)
( 32)
( 24)
MEDIAN
INORG N
55
*7
37
70
51
34
21
61
21
61
51
( 21)
' 37)
( 14)
( 26)
( 19)
( 13)
( 7)
( 22)
( 7)
< 22)
( 19)
500-
MEAN
24
5
87
37
13
61
92
11
58
76
79
SEC
( 9)
< 2)
( 33)
( 14)
( 5)
( 23)
( 35)
( 4)
< 22)
( 29)
( 30)
MEAN
CHLORA
3
IB
92
21
16
45
82
5
61
89
71
( 1)
( 7)
( 35)
( 8)
( 6)
( 17)
( 3D
( 2)
( 23)
( 34)
( 27)
15-
MIN oo
67
82
17
63
72
17
17
92
49
17
17
( 25)
( 3D
( 0)
( 24)
( 27)
( 0)
( 0)
( 35)
( 17)
( 0)
( 0)
Me. L) I AN
DISS o^rno P
30
39
51
30
13
21
84
0
63
63
76
( 10)
( 14)
I 19)
( 10)
( 5)
I 7)
( 31)
( 0)
( 21)
( 21)
( 28)
INUEX
NO
20«
259
372
2^>3
176
217
J84
169
311
390
357
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet.
Cubic meters x 8.107 x 10 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIbuTARf
INFORMATION FG* TEA AS
l "5 7 A
^ < O
LA
-------
TRIBUTARY FLOW 1NKOHHATION FUR TEXAS
12/0376
LA-CE CODE 4820
LIVINGSTON LAKE
MEAN MONTHLY FLOWS AND JAILY FLOwS(CMS)
TRIBUTARY MONTH YEAR
482081
4820C1
4820E1
4R20H1
9
10
11
12
1
2
3
u
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
ft
S
6
7
8
7<.
74
74
74
75
75
75
75
75
75
75
75
74
74
74
74
75
75
75
75
75
75
75
75
74
74
74
74
75
75
75
75
75
75
75
75
74
74
74
74
75
75
75
75
75
75
75
75
MEAN FLOW DAY
0.651
0.878
1.614
0.396
0.934
1.218
0.623
0.991
1.359
0.481
0.207
0.510
0.396
0.538
0.963
0.249
0.566
0.736
0.368
0.595
0.821
0.283
0.125
0.311
1.416
1.954
3.568
0.906
2. 067
2.690
1.388
2.209
2.973
1.019
0.453
1.133
1.699
2.039
5.097
1.048
2.464
3.823
1.671
2.605
4.248
1.218
0.538
1.331
7
4
3
7
5
9
15
5
19
21
24
7
4
3
7
5
9
15
5
19
21
24
7
4
3
7
5
9
16
6
21
24
7
4
8
5
8
15
5
17
21
13
17
FLOW DAY
O.OS1
0.014
0.595
0.396
0.396
0.283
0.147
0.142
0.170
0.079
FLOW OAY
FLOW
0.051
0.031
0.008
0.368
0.238
0.244
0.178
0.091
0.082
0.102
0.037
0.031
0.187
0.161
1.303
0.878
0.906
0.651
0.261
0.238
0.215
26
0.119
26
0.071
26
0.207
0.116
0.023 31
0.481
1.076
0.906
0.0
0.340 19
0.566
0.1SO
0.793
0.125
0.261
30.299
0.595
-------
TRIBUTARY FLOW INFORMATION FOR TEXAS U'/'J376
LA
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
^v Al. -Air. 7f-./0"Vi!
JO 36 24.C 095 01 13.0
'.ARE
DATE
FHO>'
TO
74/03/16
74/05/24
74/08/19
74/11/06
TIME DEPTH t
OF
DAY FEET
14
14
14
14
14
10
10
10
10
10
1
1
1
1
1
14
14
14
14
14
14
14
55
«55
55
55
55
?5
?5
25
25
25
05
05
05
05
05
15
15
15
15
15
15
15
0000
0005
0015
0040
0062
0000
0005
0016
0035
0060
0000
0010
0020
0035
0050
0000
0005
0015
0030
0045
0060
0070
COU10
TEMP
CENT
18.
18.
17.
16.
It.
2fc.
26.
25.
2<+.
22.
30.
29.
28.
28.
27.
23.
22.
22.
22.
22.
22.
22.
00300
DO
i
0
3
0
3
2
2
6
6
1
3
5
6
1
9
0
6
6
6
5
4
7
MG/L
9
8
6
6
9
6
H
0
9
7
1
0
0
7
7
7
7
7
7
7
.0
.8
.8
.2
.3
.2
.0
.4
.4
.4
.4
.4
.4
.6
.0
.2
.6
.2
.2
.2
llE>;Ai_£S
00300
DO
MG/L
9.0
8.8
6.6
6.2
9.3
6.2
H.O
0.4
9.4
7.4
1.4
0.4
0.4
7.6
7.6
7.2
7.6
7.2
7.2
7.2
U0077 00094
TtfftNiSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
38 242
241
238
231
230
60 323
324
323
322
376
55 415
415
411
407
406
54 283
288
288
287
286
288
288
3
00400
PH
SU
7.75
7. 70
7.40
7.10
7.10
8.95
8.9Q
8.40
7.80
7.35
9.00
8. dO
8.10
7.9Q
7.80
7.89
7.72
7.69
7.67
7.64
7.63
7.66
00-+10
T ALK
CAC03
Mb/L
70
71
72
72
74
89
89
91
90
88
92
93
93
96
96
91
92
2111202
0067
00610
NH3-N
TOTAL
Mb/L
0.040
0.050
0.040
0.040
0.060
0.060
0.050
U.OSO
0.060
0.090
0.030
0.020K
0.020K
0.020
0.020K
0.020K
0.020K
FtET DEPTH
00625
TOT KJEL
N
MG/L
0.600
0.600
0.500
0.500
0.600
0.800
0.600
0.500
0.500
0.600
1.200
0.900
1.000
1.000
1.000
0.500
0.500
00630
NO 2 & NO 3
N-TOTAL
Mb/L
0.620
0.630
0.690
0.690
0.750
0.070
0.060
0.080
0.210
0.460
0.300
0.310
0.310
0.310
0.310
0.300
0.310
00671
PHOb-DIS
OUTrlO
MG/L P
0.111
0.117
0.115
0.115
0.114
0.071
0.074
0.08S
0.107
0.143
0.104
0.091
0.091
0.089
0.086
0.076
0.081
K VALUL KNOWN TO 8E
INDICATED
-------
STOSET .-SE^IEVAL J/'T 7.S/C2/11
482001
30 3ti 24.0 095 01 18.0
LIVINGSTOl. LAKF
<*84C7
DATE
FROM
TO
7<,/03/16
74/05/2"
74/08/19
74/11/06
00665 32217 00031
TIMF DEPTH PhOS-TOT OLRP^rL INCOT LT
OF A HEMNING
DAY FEET
14
14
14
14
14
10
10
10
10
10
11
11
11
14
14
14
14
14
14
14
55
55
SS
55
•F5
25
?5
25
25
?5
05
05
05
15
15
15
15
15
15
15
0000
0005
0015
0040
0062
0000
0005
0016
0035
0060
0000
0010
0016
0000
0005
0015
0030
0045
0060
0070
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
').
0.
0.
0.
0.
0.
0.
0.
P UG/L PERCENT
163 ?4.9
163
167
167
190
110 5.0
121
115
136
198
19.7
143 12.9
134
131
130
127
113
128
1.0
5.0
1.0
11EPAIES
3
2111202
0067 FEET
DEPTH
-------
STORET J£TRI£VAL DATE 76/02/1i
482002
30 3<* 29.0 095 Ob 34.0
Tt'AAb
DATE
FROM
TO
74/03/16
74/05/24
74/08/19
74/11/07
TIME
OF
DAY
14
14
14
14
14
11
11
11
11
11
10
10
10
10
10
12
12
12
12
12
12
25
?5
25
25
?5
00
00
00
00
00
30
30
30
30
30
10
10
10
10
10
10
DEPTH
FEET
0000
0005
0015
0030
0060
0000
0005
0015
0035
0055
0000
0015
0030
0050
0064
0000
0005
0015
0030
0045
0058
00010
*ATER
TEMP
CENT
18.5
18.2
17.8
17.6
14.3
26.8
26. <•
?6.0
25.0
21.3
29.4
29.0
28.4
28.2
26.0
20.7
20.8
20.7
20.7
20.7
20.7
lltPALES
00300
DO
MG/L
8.8
9.0
8.0
4.0
7.4
6.8
2.4
0.5
7.2
1 .4
0.0
0.0
0.0
7.6
7.6
7.4
7.2
7.8
7.4
00077 00094
TRANSP CNDUCTVY
SECCHl FIELD
INCHES MIC^OMHO
32 245
245
241
244
237
48 350
349
321
320
276
62 416
419
414
413
427
28 260
256
258
260
262
260
3
00400
Ph
Su
7.60
7.65
7.60
7.40
6.85
8.90
8.70
8.55
7.60
7.35
8.60
7.90
7.65
7.60
7.30
7.80
7.71
7.75
7.75
7.76
7.74
00410
T ALK
CAC03
MG/L
75
77
77
69
73
94
93
88
89
91
'
90
90
90
90
88
69
2111202
0066
00610
NH3-N
TOTAL
MG/L
0.060
0.050
0.040
0.050
0.060
0.040
0.060
0.060
0.070
0.180
0.060
0.020K
0.030
0.020K
0.030
0.02UK
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.600
0.700
0.700
0.500
0.600
0.900
0.700
0.600
0.500
0.600
0.800
0.500
0.600
0.700
0.600
0.500
00630
N02&N03
N-TOTAL
MG/L
0.640
0.630
0.630
0.620
0.880
0.090
0.120
0.080
0.290
0.380
0.240
0.240
0.230
0.230
0.230
0.230
00671
PiOS-uIS
O-^THO
MG/L P
0.123
0.121
0.119
0.118
0.124
0.100
0.107
0.094
0.129
0.184
0.119
0.126
0.115
0.113
0.120
0.113
K VALUE KNOWN TO dt
LESS THAN INDICATEJ
-------
4&2002
30 39 29.0 095 06 34.0
LIVINGSTON ' 4KE
48407 TEXAS
-Ate
DATE
FROM
TO
7u/03/16
74/05/24
74/08/19
74/11/07
00665 32217 OG031
TIME OtPTH PHOS-TOT CrlLRPHYL IN'CDT LT
OF A REMMlNG
DAY FEET
14
14
14
14
14
11
11
11
11
11
11
10
10
10
12
12
12
12
12
12
25
?5
25
25
25
00
00
00
00
00
00
30
30
30
10
10
10
10
10
10
0000
0005
0015
0030
0060
0000
0005
0009
0015
0035
0055
0000
0009
0013
0000
0005
0015
0030
0045
0053
MG/L P
0,
0
0.
0,
0,
0,
y ,
0.
0,
0,
0,
0.
0,
0,
0,
0,
.179
.174
,171
.166
.221
.150
.163
.124
.170
.220
.172
,171
.161
.156
.156
.145
UG/L PERCENT
46.3
5.2
"
1.0
22.3
5.0
1.0
15.8
2111202
0066 FEET
DEPTH
-------
KET^lEVAt. QftTf 76/.02/11
30 4<« 06.0 095 03 38.0
LIVlKoSTON LAKE.
DATE
FROM
TO
74/03/16
74/05/24
74/08/19
74/11/07
DATE
FROM
TO
74/03/16
7<«/05/24
74/08/19
74/11/07
TIMF DEPTH
OF
DAY FEET
13 55 0000
13 55 0005
13 55 0015
13 55 0025
13 55 0050
1 30 UOOO
1 30 0005
1 30 0015
1 30 0025
1 30 0035
11 30 0051
14 35 0000
14 35 0005
14 35 0015
14 35 0030
14 35 0040
14 35 0052
12 55 0000
12 55 0005
12 55 0015
TIME DEPTH
OF
DAY FEET
13 55 0000
13 55 0005
13 55 0015
13 55 0025
13 55 0050
30 0000
30 0005
30 0006
30 0015
30 0025
30 0035
11 30 0051
14 35 0000
14 35 0009
12 55 0000
1? 55 0005
12 55 0015
03010
WATER
TEMP
CENT
18.4
18.3
18.1
18.2
16.6
27.7
27.4
26.9
26.7
26.0
21.9
31.0
29.8
29.0
28.1
27.9
27.4
21.2
21.6
21.6
00665
PHOS-TOT
MG/L P
0.190
0.188
0.195
0.216
0.333
0.162
C.I 58'
0.159
0.173
0.188
0.227
0.220
0.218
0.210
00330 00077 00094
DO TRANS^ CNDuCTVY
StCCHl FIELD
MG/L INCHES M
24
a.o
a.o
7.8
4.4
4«
7.9
6.7
4.9
3.U
C.8
10.4 54
9.2
4.6
0.4
0.2
0.4
5.0 38
7.2
6.8
32217 00031
CHLKPHYL INCDT LT
A REMNING
JG/L PERCENT
27.6
6.7
1.0
28.0
1.0
14.0
CrtOMHO
250
250
255
264
297
394
394
390
390
384
330
434
431
433
469
459
445
279
280
280
lit- ALE 5
3
00400 00410
PH T ALK
CACO3
SU
7.80
7.70
7.65
7.55
7.10
9.00
8.90
a. 60
8.00
7.70
7.40
8.90
8.90
8.40
7.70
7.60
7.55
7.51
7.53
7.49
MG/L
77
77
77
78
86
96
99
99
100
101
92
91
88
89
2111202
0056 FEET DEPTH
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PHOS-OIS
TOTAL N N-TOfAL OKTriO
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.050
.050
.060
.070
.140
.070
.040
.060
.100
.100
.390
.020K
.020
.020K
MG/L
0.700
0.700
0.600
0.700
0.800
1.000
0.800
0.700
0.600
0.700
0.800
0.700
0.600
0.600
MG/L
0.640
0.640
0.650
0.680
0.940
0.160
0.130
0.200
0.270
0.380
0.270
0.370
0.390
0.390
MG/L P
0.130
0.127
0.133
0.148
0.235
0.106
0.105
0.115
0.128
0.146
0.215
0.174
0.170
0.173
K VALUE *NO«N 70 BE
-------
KET3IEV4L DATE 76/02,'il
482004
30
-------
WETfCEVAL OATt 76/02/51
JO 47 47.0 095 09 0-y.O
LIVINGSTON t_4Kt
43<»0? TE AS
DATE
FPOM
TO
74/03/16
74/05/24
74/08/19
74/11/07
DATE
FROM
TO
74/03/16
74/05/24
74/OU/l1^
74/11/07
TIME DEPTH
OK
OAY FEET
10 55
10 55
10 55
10 55
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 50
13 50
13 50
13 50
13 50
13 50
TIME
OF
DAY
10 55
10 55
10 55
10 55
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 50
13 50
13 50
13 50
13 50
13 50
0000
0005
0015
0022
0000
0005
0015
0035
0045
0055
0000
0005
0015
0030
0046
0000
0005
0015
0030
0045
0056
DEPTH
FEET
0000
0005
0015
0022
0000
0005
0006
0015
0035
0045
0055
0000
0009
0000
0005
0015
0030
0045
0056
00010
WATER
TEMP
CENT
19.0
19.0
19.0
18.9
29.1
27.3
26.9
26.6
26.5
25.4
31.2
30.5
29.6
28.5
27.9
20.6
20.7
20.7
20.6
20.6
20.5
00665
PHOS-TOT
MG/L P
0.238
0.241
0.242
0.254
0.165
0.179
0.194
0.230
0.241
0 .244
0.472
0.490
0.478
0.434
0.495
0.469
00300 00077 0009*
DO TRaNSP CNOUCTVY
SECCHl FIELD
MG/L INCHES M1CKOMHO
35
8.6
8.6
8.0
30
7.?
4.8
2.0
1.7
1.3
9.0 42
8.2
3.2
0.4
0.4
5.0 11
• 5.6
5.0
5.4
5.8
5.8
32217 00031
CHLRPHYL INCDT LT
A KEMNING
UG/L PERCENT
7.3
5.7
1.0
21.3
1.0
7.1
306
310
308
308
405
403
407
415
415
419
458
451
456
48fa
497
289
304
294
296
339
332
UEPiLES
3
00400 00410
PH r ALK
CAC03
SU
7.90
7.90
7.80
7.80
9.15
8.55
7.80
7.45
7.35
7.30
8.90
8.80
8.10
7.60
7.50
7.24
7.26
7.21
7.20
7.22
7.23
M13/L
ai
81
81
83
92
96
98
100
101
103
74
76
75
79
87
84
2111202
0056 FEET DEBTn
00610 00625 00630 00671
NH3-N TOT KJEL N02S.N03 PnOS-UIS
TOTAL N N-TOTAL OWTHO
MG/L
0.060
0.060
0.060
0.060
0.060
0.070
0.080
0.070
0.070
0.07C
0.060
0.060
0.060
0.060
0.050
0.060
MG/L
0.800
0.800
0.800
0.800
1.100
0.800
0.700
0.600
0.700
0.700
0.700
0.700
0.600
0.800
0.700
0.700
MG/L
0.670
0.660
0.660
0.680
0.160
0.480
0.740
0.780
0.930
1.040
0.960
1.050
1.050
1.250
1.250
1.350
MG/L P
0.176
0.178
0.178
0.132
0.098
0.119
0.142
0.178
0.186
0.188
0.344
0.369
0.353
0.372
0.397
0.342
-------
RETRIEVAL OAIE 76/e?'ii
483006
30 50 i.O
LIVINGSTON LAKE
484!"; 7 1 r>Ai
i
»
1EH.
5LES
3
DATE
FROM
TO
74/03/16
74/05/24
74/08/19
74/11/07
DATE
FROM
TO
74/0 3/ 16
74/05/24
74/08/19
74/11/07
U*E DE»TH
OF
DAY FEET
11 15 0000
11 15 0005
11 15 0015
11 15 0023
16 00 0000
16 00 0005
16 00 0015
16 00 0035
16 00 0049
12 05 0000
12 05 0005
12 05 0015
12 05 0035
12 05 0051
14 30 0000
14 30 0005
14 30 0020
TIME DEPTH
OF
OAV FEET
11 15 0000
11 15 0005
11 IS 0015
11 15 0023
16 00 0000
16 00 0005
16 00 0015
16 00 0035
16 00 0049
12 05 0000
12 05 0007
14 30 0000
14 30 0005
14 30 0020
00010
»ATER
TEMP
CENT
19.7
19.7
19.7
18.9
29.6
28.9
27.6
26.6
26.0
30.4
30.2
29.4
28.0
27.8
20.8
20.7
20.7
00665
PHOS-TOT
MG/L P
0.281
0.267
0.399
0.389
0.226
0.197
0.207
0.255
0.267
0.384
0.373
0.330
00300 00077
DO TrtANSP
SECCHI
MG/L INCHES
30
9.0
8.6
5.0
24
11.2
5.2
1.9
1.4
6.8 36
4.4
0.2
0.0
.0.4
4.6 10
4.0
4.6
32217 00031
CHLRPHYL INCDT LT
A PEMNING
UG/L PERCENT
12.2
42.9
1.0
26.1
1.0
2.8
00094
CNOUCTVY
FIELD
M1CROMHO
336
336
338
371
415
420
418
421
420
478
479
487
535
540
233
233
245
00400
PH
su
8.
8.
7.
7.
9.
9.
7.
7.
7.
8.
8.
7.
7.
7.
7.
7.
6.
15
30
30
20
35
10
75
40
40
75
10
60
55
55
07
06
98
00410
T AL*v
CAC03
MG/L
69
89
93
92
99
100
103
107
108
69
67
70
211
0027
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.160
0.160
U.060
0.06C
0.080
0.060
0.07C
0.080
0.080
0.070
1202
FEET OEPTrt
00625
TUT KJEL
N
MG/L
1.000
1.000
1.000
0.900
1.500
1.400
0.700
0.500
0.500
0.800
0.700
0.600
00630
N02&N03
N-TOTAL
MG/L
0.380
0.370
0.910
0.900
0.180
0.21C
0.620
1.15U
1.070
0.540
0.530
0.550
00671
PnOS-OIS
ORTHO
MG/L P
0.178
0.172
0.308
0.304
0.069
0.079
0.141
0.197
0.175
0.230
0.232
0.245
-------
ir.'AL CAT-: 7h/C,?/H
<«82007
JO 5-t 50.0 095 16 13. U
LIVINGSTON _A
-------
STORET RETRIEVAL DATE 76/02/11
482U04
30 54 10,0 095 17 31.0
LIVINGSTON uAKE.
DATE
FROM
TO
74/03/16
74/05/34
74/08/19
74/11/07
DATE
FROM
TO
74/03/16
74/05/24
74/08/19
74/11/07
TIME
OF .
DAY
13
1J
13
13
13
15
15
15
15
15
10
10
10
10
10
10
15
15
20
20
20
20
20
05
05
05
05
05
50
50
50
50
50
50
00
00
TIME
OF
DAY
13
13
13
13
13
15
15
15
15
15
10
10
15
15
20
20
20
20
20
05
05
05
05
05
50
50
00
00
DEPTH
FEET
0000
0005
0015
0025
0037-
0000
0005
0015
0025
0035
0000
0005
0015
0025
0035
0041
0000
0005
DEPTH
FEET
0000
0005
0015
0025
0037
0000
0005
0015
0025
0035
0000
0004
0000
0005
00010
HATER
TEMP
CENT
19.6
19.6
19.4
19.4
19.3
29.5
28.7
26.9
26.8
26.7
30.5
30.0
29.1
28.5
28.3
27.8
20.7
20.7
00665
PHOS-TOT
MG/L °
0.526
0.556
0.588
0.582
0.570
0.241
0.182
0.2*0
0.243
0.246
0.425
0.420
00300 00077 00094
DO TRANSP CNOUCTVY
SECCHI FIELD
MG/L INCHES MICROMrtO
24
5.8
6.0
5.6
5.8
30
9.2
3.2
2.6
1.0
6.6 36
4.2
0.4
0.4
0.2
0.4
5.8 6
6.2
32217 00031
CHLRPHYL INCDT LT
A KEMNING
UG/L PERCENT
12.1
10.4
1.0
26.1
1.0
3.4
440
444
447
444
443
436
<*35
427
425
428
608
595
606
720
709
617
186
184
llEr
3
00400
PH
su
7.65
7.50
7.45
7.40
7.40
9.50
8.70
7.55
7.50
7.45
8.40
8.10
7.70
7.70
7.70
7.60
7.46
7.40
AuES
00410
T ALK
CAC03
MG/L
108
109
110
110
112
109
109
107
109
111
62
60
211
0042
00610
NH3-N
TOTAL
MG/L
0.090
0.090
0.110
0.100
0.100
0.050
0.060
0.110
0.09U
0.110
0.060
0.060
1202
FEET OEP
00625
TOT (VJEL
N
MG/L
1.100
1.100
1.100
1.000
0.800
1.900
1.000
0.700
0.700
0.700
0.700
0.600
Tri
00630
NU2«.N03
N-TOTAL
MG/L
1.430
1.400
1.490
1.520
1.51U
0.110
0.430
0.830
0.940
0.940
0.350
0.350
00671
HrtOS-DIS
ORTHO
MG/L P
0.436
0.451
0.470
0.452
0.443
0.065
0.095
0. 166
0.184
0.183
0.184
0.201
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL DATE 7&/OJ/10
DATE TIME DEPTH N02&N03
FHUM ' OF
TO DAY FEET
74/09/07
74/10/04
74/11/03
74/12/08
75/01/05
75/02/09
75/03/16
75/04/06
75/04/26
75/05/19
75/06/21
75/06/17
19 30
19 00
09 45
13 30
09 45
10 30
10 30
10 00
09 30
10 00
13 45
19 30
4e?OAl
30 37 15.0 095 00 J5.0 4
48085 7.5 CAMILLA
O/LIVINGSTONE
100 FT M OF HrtY 222 3.5 MI NE OF CAMILLA
11EPALES 21112U4
0000 FEET OEHTH CLASS oO
0630
I&N03
OTAL
IG/L
0.016
0.320
0.336
0.336
0.416
0.504
0.540
0.480
0.390
0.600
0.420
0.035
00625
TOT KJEL
N
MG/L
o.eoo
0.700
o.eoo
1.300
0.600
1.200
0.650
1.100
1.000
2.600
1.200
0.700
00610
Nr13-N
TOTAL
MG/L
0.025
0.030
0.095
0.04B
0.016
0.216
0.090
0.165
0.072
0.240
3.050
0.075
00671
PHOS-DIS
ORTHO
MG/L P
0.105
0.100
0.090
0.120
0.110
0.120
0.095
0.105
0.090
0.100
0.095
0.165
00665
PHOS-TOT
MG/L P
0.120
0.130
0.120
0.180
C.160
0.150
0.140
0.147
0.150
0.150
0.170
0.220
-------
ST'JHLT HtTRlEVAL DAlc 7b/03/iO
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/09/07
74/10/04
74/10/31
74/12/oe
75/01/05
75/08/09
75/03/16
75/0<«/05
75/04/19
75/05/17
75/05/31
75/06/21
75/07/13
75/08/17
IS 00
09 30
12 30
09 30
08 45
11 45
10 50
10 00
11 15
10 00
09 05
08 30
10 20
10 00
V-J20A2
30 56 00.0 095 30 10.0 4
TRI
-------
RETRIEVAL DATE 7b/G.VlG
30 *b 12.0 095 1* 33.0 4
PALMETTO CK^EK
«»8 7.5 CARLISLE
I/LIVINGSTONE KEStr^VOIR
HrtY 980 BRDC- 5.0 MI NW JCT
11E->ALES
oooo KEET DEPTH
ri US RT 190
211120*
CLASS oo
DATE
FROM
TO
7*/09/07
7*/10/0*
7*/ll/03
7*/12/07
75/01/05
75/U2/09
75/03/15
75/0*/05
75/0*/26
75/05/19
75/06/21
75/08/2*
TIME
OF
DAY
20 ?0
19 30
10 43
10 35
11 00
11 30
12 no
12 00
13 00
11 00
12 30
oa 30
FEET
C0630
N02«.NOJ
N-TOTAL
MG/L
0.0*0
0.016
0.056
0.056
0.072
0.080
0.005
0.005
0.015
0,025
0.0*0
0.005
00625
TOT KJEL
N
MG/L
o.*oo
o.*oo
0.600
1.100
0.900
1.100
0.550
0.550
0.350
1.050
O.*00
0.900
00610
NH3-N
TOTAL
MG/L
0.110
0.010
0.090
0.032
0.032
0.073
0.0*0
0.070
0.015
0.175
0.020
0.035
00671
PHOS-DIS
ORTHO
MG/L P
O.OOSK
0.017
0.025
0.02*
0.020
0.020
0.020
0.015
0.020
0.020
0.027
0.010
OT665
i-'HOS-TOT
MG/L P
0.006
0.017
0.050
0.0*0
0.0*0
0.030
0.020
0.020
0.050
0.030
0.0*0
0.010
K VALUE KNOWN TO dE
LESS THAN INDICATED
-------
STO*LT RETRIEVAL OATt 76/03X10
DATE TIME DEPTH N02«.N03
FROM OF
TO DAY FEET
74/09/07
74/10/04
74/11/03
74/12/07
75/01/05
75/02/09
75/03/15
75/04/05
75/04/26
75/05/19
75/06/21
75/08/24
21 10
20 00
12 00
10 20
11 30
12 30
12 20
12 30
14 00
12 00
11 20
09 30
4B20C1
30 49 30.0 095 19 15.0 4
c CAHOLINA CREEK
•*8 7.5 STALLV
T/LWINGSTONE REStrfVOlfc
2NOHY M BPOG 2.5 Ml E
UE^ALES
JCT * HWY 9PO
2111204
0000 FEEf DEPTH CLASS 00
0630
!«.N03
OTAL
IG/L
0.012
U.016
0.008
0.008
0.016
0.016
0.005
0.010
0.015
0.015
0.015
0.010
00625
TOT KJEL
N
MG/L
0.600
0.400
0.500
1.100
0.700
0.900
0.250
1.050
1.150
1.200
0.550
0.700
00610
NH3-N
TOTAL
MG/L
0.060
0.010
0.030
0.032
0.024
0.032
0.010
0.030
0.030
0.125
0.040
0.020
00671
PHOS-OIS
ORTHO
MG/L P
0.020
0.015
0.020
0.016
0.010
0.016
0.010
0.010
0.020
0.015
0.015
0.015
00665
PHOS-TOT
MG/L P
0.020
0.015
0.030
0.030
0.030
0.020
0.020
0.010
0.020
0.020
0.020
0.020
-------
SETK1EVAL OATE 76/03/10
DATE TIME DEPTH N02NN03
FROM OF
TO DAY FEET
74/09/07
74/10/04
74/11/03
74/12/07
75/01/05
75/02/09
75/03/16
75/04/06
75/04/26
75/05/19
75/06/21
75/08/24
21 30
20 15
12 30
10 15
11 35
13 00
12 45
12 40
13 30
12 00
11 00
10 30
30 49 30.0 095 20 10.0 4
» CAKOLINA CREEK
43 7.5 STALEY
T/LIVINGSTONE «ESEKVOIrf
2.NQKY KD dhOG 1.9 MI E
0000 FEET DEPTH
JOT W HWY
2111204
CLASS 00
960
0630
INN03
OTAL
IG/L
o.oia
0.040
0.024
0.008
0.016
0.016
0.010
0.005
0.020
0.015
0.015
0.005
006?5
TOT KJEL
N
MG/L
0.700
0.900
0.700
1.100
0.900
0.900
0.600
0.800
1.200
1.150
0.700
1.100
00610
NH3-N
TOTAL
MG/L
0.060
C.015
0.050
0.080
0.024
0.024
0.030
0.045
0.075
0.180
0.030
0.025
00671
PhOS-DIS
ORTHO
MG/L P
0.155
0.020
0.075
0.040
0.055
0.046
0.010
0.010
0.030
0.050
0.020
0.010
00665
PHOS-TOT
MG/L P
0.1 60
0.035
0.120
0.060
0.100
0.070
0.020
0.030
0.050
0.080
0.040
0.040
-------
RETRIEVAL SATE /fc/03/10
4b20El
30 49 15.0 095 29 15.0 4
HAMrfON Rive
48 ufALKEff CO HAP
T/L1VINGSTONE RESEKVOIr?
SAMP E'\0 P.D 1.6 MI b£ JCT rUY 980
0000 FEET DEPTh CLASS 00
DATE
FROM
TO
74/09/07
74/10/04
74/1 1/03
74/12/07
75/01/05
75/02/09
75/03/16
75/04/06
75/04/26
75/06/21
75/08/24
00630 00625
TIME DEPTH •J02J.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
24
22
13
09
13
14
13
13
14
10
11
00
00
00
00
00
00
?0
00
50
00
30
MG/L
1.
1.
U.
0.
0.
o.
0.
0.
1.
0.
260
600
610
464
600
528
990
980
150
410
MG/L
2.
1.
1.
3.
1.
3.
3.
1.
2.
3.
1.
500
700
400
800
600
000
600
600
700
300
650
00610 00671 00665
NH3-N PHOS-DIS PriOS-TOT
TOTAL ORTriO
MG/L
1.
0.
0.
0.
c.
1.
1.
0.
1.
0.
0.
450
420
250
630
336
250
920
030
100
920
105
MG/L
1.
1.
0.
0.
0.
0.
1.
0.
1.
0.
1.
p
880
880
655
640
430
B20
650
040
300
500
950
MG/L P
1.880
1.900
0.690
1.050
0.540
0.^10
l.faOO
C.270
1.320
0.660
2.300
-------
STOKLl RETRIEVAL DATE 7o/03/10
4820F1
30 56 25.0 095 26 bcS.O 4
46 7.5 TKIMTY w
T/LIVINGSTONE *E5Er
-------
RETRIEVAL OATE 76/03/10
30 51 15.0 095 03 35.0 4
KOOf CREEr
n8 7.5 ONALA5KA
T/L WINGSTONE r5ESe^VGI&
N Or DIRT *Q 2.5 MI N OF CO RO 3152 JCT
llt-^LES 21112C<.
0000 FEET OEPTh CLASS 00
DATE
FROM
TO
74/0^/07
74/10/04
74/10/31
74/12/08
75/01/05
75/02/08
75/0^/19
75/05/17
75/06/21
75/08/17
TIME i
OF
DAY 1
12 ?0
11 35
14 15
11 30
11 45
13 55
10 00
11 50
10 45
11 45
FEET
00630
N02&N03
N-TOTAL
MG/L
0.028
0.008
0.032
0.016
0.016
0.016
0.015
0.010
0.010
0.010
00625
TOT KJEL
N
MG/L
0.700
0.500
0.700
0.600
0.800
0.500
i.eoo
1.075
0.550
0.512
00610
NH3-N
TOTAL
MG/L
0.060
0.015
0.055
0.024
0.06*
C.064
0.220
0.040
0.015
0.025
00671
PriOS-DIS
ORTHO
MG/L P
0.010
0.005
0.015
0.008
0.005K
o.ooe
0.010
0.005
0.010
0.010
00665
PriOS-TOT
MG/L P
0.027
0.010
0.060
0.030
0.020
0.020
0.020
0.025
0.030
0.040
K VALUE KNO*N TO BE
LESS THAN INDICATED
-------
bTOSET REIR1EVAL DATE 7t>/03/13
4820J1
30 52 15.0 095 04 30,0 4
KICKAPOO CkcEK
<*6 7.5 ONALASKA
T/LIVlNGSTONE KEStKVUlK
BANK w OF DIRT no 3.3 MI N OF FM3152 jcr
llE^ALES 2111204
0000 FEET DEr-Tn CLASS 00
DATE TIME DEPTH N02S.N03
FrtOM OF
TO DAY FEET
74/09/07
74/10/04
74/10/31
74/12/08
75/01/05
75/02/08
75/03/15
75/04/05
75/04/19
75/05/17
75/06/21
75/08/17
11 50
11 50
13 50
11 10
12 00
13 40
12 15
11 05
10 00
11 30
10 15
11 ?S
i0630
:S.N03
OTAL
IG/L
0.028
0.024
0.032
0.048
0.040
0.064
0.015
0.010
0.015
0.015
0.005
0.010
00625 .
TOT KJEL
N
MG/L
0.800
0.900
0.600
1.000
l.?00
0.600
0.600
0.450
1.350
1.050
0.750
0.750
00610
NH3-N
TOTAL
MG/L
0.055
0.022
0.040
0.192
0.040
0.048
0.060
0.070
0.250
0.025
0.015
0.020
00671
PHOS-DI5
-ORTHO
MG/L P
0.065
0.085
0.075
O.ObO
0.040
0.064
0.005
0.005K
0.040
0.035
0.050
0.070
00665
PHOS-TOT
MG/L P
0.115
0.1 3u
0.130
0.140
0.140
0.090
0.010K
0.010K
0.060
0.060
0.110
0.130
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/04/27
4820KA A54820RA PG03050
30 56 30.0 095 55 00.0 4
MADISONVILLE
48 7.5 MAUISONVILLE
T/LIVINGSTONE RES. 130391
CANEY CR. TO TRINITY RIVER
11EPALES 2141204
OCOO FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/19
75/03/20
75/04/10
75/04/28
75/05/28
75/06/20
75/07/07
75/07/24
75/08/19
75/09/22
75/11/06
75/12/05
76/01/06
00630
TIME DEPTH N02J.N03
OF N-TOTAL
DAY FEET
15
23
09
08
14
09
10
15
16
10
11
08
10
10
50
00
55
00
20
45
30
00
45
20
20
35
MG/L
7
0
0
0
0
0
0
0
11
.600
.900
.025
.050
.050
.100
*150
.075
.500
00625
TOT KJEL
N
MG/L
96.000
21.000
325.000
280.000
320.000
7.950
26.000
36.000
30.000
2.500
14.000
6.800
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
2.930
1.440
20.000
2.600
14.500
21.000
12.600
0.038
0.230
0.155
MG/L P
8.750
9.800
30.000
1.500
4.700
5.900
2.100
4.500
9.200
5.900
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P 1NST
29.000
53.000
82.500
110.000
116.000
2.180
5.450
7.000
2.600
4.500
11.800
7.000
0
0
0
0
0
0
0
0
0
0
0
0
0
MOD MONTHLY
.100
.100
.195
.098
.156
.183
.578
.143
.132
.132
.900
.070
.861
0.200
0.100
0.130
0.100
0.231
0.182
0.191
0.132
0.153
0.174
0.300
0.125
0.923
-------
STOREf RETRIEVAL, OAT£ 7o/04/27
DATE
FROM
TO
74/09/23
CP(T)-
74/09/23
74/10/30
CP(T)-
74/10/30
75/01/08
CP(T>-
75/01/08
75/01/20
CP(T>-
75/01/20
75/02/06
CP(T>-
75/02/06
75/03/28
CP-
75/03/28
75/04/21
CP < T ) -
75/04/21
75/05/12
CPU>-
75/05/12
75/06/12
75/08/26
CP(T)-
75/08/26
75/09/22
CP (T) -
75/09/22
75/12/05
CP(T)-
75/12/05
75/12/22
CP(T>-
75/12/22
00630
TIME DEPTH N02^N03
OF N-TOTAL
DAY FEET MG/L
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
13
11
16
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
0.140
0.560
0.080
0.880
0.320
0.550
0.400
0.325
0.075
0.075
0.275
00625
TOT KJEL
N
MG/L
24.500
17.000
18.000
17.000
4.480
18.000
27.000
15.500
21.000
15.000
33.000
28.000
22.000
4320WA AS4820WA P003000
30 58 30.0 095 22 30.0 4
TRINITY
48 7.5 TRINITY E T*
T/LIVINGSTON RES 120391
BELLS BRANCH t/ilITE ROCK CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-DIS. PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOw-MGO
MG/L MG/L P MG/L P INST MGD MONTHLY
11.000
2.240
13.500
15.000
7.600
5.000 4.100
4.700 4.200
9.250
4.200
0.163
5.500 0.185
3.700 3.700 6.200 0.252
5.700 4.700 6.800 0.185
3.500 0.175
0.200
0.200
0.210 0.200
0.180
3.100 3.500 0.185 0.175
0.200
0.175
3.000 2.900 3.500 0.250 0.200
6.400 5.000 6.200 0.216 0.196
4.700 3.500 3.800 0.017 0.019
7.100 7.700 0.185 0.200
12.600 7.500 9.300 0.230 0.200
7.400 5.400 7.200 0.200 0.185
-------
STGKET RETRIEVAL DATE 76/0'»/2?
DATE
FROM
TO
74/08/15
CP(T)-
74/08/15
74/09/16
CP < T ) -
74/09/16
74/10/15
CPU)-
74/10/15
74/11/15
CP(T)-
74/11/15
74/12/16
CPU)-
74/12/16
75/01/15
CP-
75/01/15
75/02/17
CP(T)-
75/02/17
75/03/14
CP-
75/03/14
75/04/15
CP < T > -
75/04/15
75/05/15
CP(T>-
75/05/15
75/06/16
CP < T ) -
75/06/16
75/07/16
CP(T>-
75/07/16
00630 . 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
1
4
4
3
2
1
2
2
1
2
3
3
.680
.000
.500
.680
.400
.920
.030
.080
.760
.800
.900
.000
17
11
17
16
14
21
23
23
18
20
15
15
.000
.300
.000
.000
.800
.000
.000
.000
.000
.000
.500
.000
4820XA TF4820XA P020000
30 44 00.0 095 33 00.0 4
HONTSVILLE M
48 7.5 HUNTSVILLE
T/LIVINGSTONE RES 120391
TOriN BRANCH
.11EPALES 2141204
0000 FEET DEPTH CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLO«-MGD
MG/L MG/L P MG/L P INST MGD MONTHLY
1.050
1.950
6.500
7.400 9.225
0.640 6.000
1.950 6.000
5.300 5.800
2.600 6.900
7.350
4.900 6.300
7.200
5.900 6.100
7.100
5.600 5.500 7.400
5.795 6.095 7.300
0.480 6.900
3.300 5.500 6.700
8.075
1.880 6.000 6.650
-------
STORET RETRIEVAL DATE 76/0'V27
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/03/06
75/03/20
75/04/03
75/04/16
75/04/30
75/05/1*.
75/05/28
75/06/11
75/07/02
75/07/14
75/11/11
75/12/15
11 45
10 00
11 00
15 00
11 30
14 00
09 00
13 30
11 00
15 30
09 00
09 00
4820YA PD4820YA P000670
31 02 00.0 096 07 00.0 4
NORMANGEE
48 7.5 NORMANGEE
T/LIVINGSTONE RES 120391
HILLIS CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
>0630
I&N03
OTAL
IG/L
6.600
3.700
4.800
4.300
4.500
0.050
2.800
0.750
0.025
0.075
2.200
00625
TOT KJEL
N
MG/L
3.000
7.400
2.800
2.000
2.200
10.000
2.000
3.400
2.800
15.000
10.000
00610
NH3-N
TOTAL
MG/L
0.110
0.050K
0.120
0.050K
5.000
0.079
0.025K
0.450
1.570
5.100
00671
PHOS-DIS
ORTHO
MG/L P
1.230
2.700
3.400
2.200
1.600
1.450
0.410
0.300
1.450
7.200
00665
PHOS-TOT
MG/L P
2.300
2.100
2.900
4.300
2.200
1.800
2.100
1.100
0.480
2.900
8.300
50051
FLOW
RATE
INST MGD
0.038
0.025
0.025
0.025
0.030
0.039
0.030
0.030
0.025
0.025
0.025
0.028
50053
CONDUIT
FLOW-MOD
MONTHLY
0.030
0.028
0.028
0.028
0.028
0.045
0.030
0.030
0.028
0.025
0.025
0.025
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
STORCT fiETRIEVAL DATE 76/04/27
4820ZA PD<»820ZA P002000
30 42 06.0 095 33 00.0 4
TX OEPT CGr-
75/02/10
75/03/10
CP(T)-
75/03/10
75/04/25
75/05/06
75/06/17
75/07/07
75/08/21
75/09/22
00630
N-TOTAL
MG/L
0.120
0.080
2.320
3.430
5.520
4.160
11.200
3.150
0.800
1.100
0.600
0.150
2.400
00625
TOT KJEL
N
MG/L
9.000
19.000
5.500
10.000
7.800
11.200
13.000
12.000
11.000
7.800
12.000
17.250
12.500
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOw-MGD
MG/L MG/L P MG/L P INST MGD MONTHLY
0.025K
0.110
0.050K
0.117
0.050K
0.050K
0.080K
0.580
1.200
0.2SO
0.025
0.405
0.025K
3.540
3.300
3.600
3.600
4.400
4.900
18.400
4.800
6.600
4.800
4.200
4.800
3.900
4.300
4.600
4.100
4.700
4.800
5.600
18.400
5.900
6.900
5.300
5.000
5.700
4.900
0.190
0.208
0.223
0.200
0.208
0.200
0.183
0.160
0.208
0.160
0.108
0.180
0.285
0.250
0.210
0.232
0.200
0.230
0.200
0.176
0.183
0.200
0.172
0.114
0.190
0.265
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
STOfttT RETRIEVAL DATE
4*2031 AS482031
30 57-00.0 095 20 45.0 4
oALLGwAYS ''AKINA
48 7.5 rtYSEN dOTTOM
D/LAKE LIVINGSTON
LAKt LIVINGSTON'
P000200
lltPALtS
2141204
0000 FEET DEPTH CLASS 00
DATE
FRQH
TO
74/09/26
74/ 10/29
74/11/25
74/12/19
75/01/30
75/02/25
75/03/27
75/05/22
75/06/26
75/07/17
75/08/65
TIME DEPTH
OF
DAY FEET
10 50
14 OQ
09 05
09 20
10 00
09 30
14 00
HO 20
H ^
22 45
10 00
00630
N02&N03
N-TOTAL
MG/L
49.600
3S.OOO
33.600
36.800
1.520
60.000
78.000
51.000
77.000
51.000
00625
TUT KJEL
N
MG/L
1.300
i.ooo
1.100
3.000
3.000
2.800
1.20C
3.000
3.100
1.800
3.400
00610
NH3-N
TOTAL
MG/L
0.038
0.210
0.050K
0.123
0.050K
0.180
C.170
Ol210
n.iio
0^125
0.130
00671
PriOS-OIS
ORTHO
MG/L P
8.500
9.250
5.000
4.600
14.500
7.600
10.500
7.150
00665
PMOS-TOT
MG/L P
8. (300
9.250
6.300
5.300
4; 625
7.700
7.100
14.500
7.600
10.600
7.480
50CS1
FLOW
RATE
INST MQD
0.002
0.001
6.002
0.001
0.0001
0.001
0.001
0.0001
0.002
0^002
0.009
50053
CONDUIT
FLOw-MGO
MONTHLY
0.001
0.0005
0.003
0.001
0.001
0.001
o.ooos
0.0005
o.ooi
0.001
0.001
)< VALUE KNQWN TO BE
LESS THAN INDICATED
-------
STOHET RETRIEVAL OAIi. 7&/03/10
H000300
30 40 00.0 095 00 00.0 4
MEMORIAL FuI'jT
48 7.b 0'NALAS.^.A Tx,
U/LlVlNGSTOME
LIVINOSTONu
00630
DATE TIME DEPTH N02&N03
F«OMV OF N-TOTAL
TO DAY FEET MG/L
74/09/26
74/10/24
74/11/26
74/12/19
75/01/30
75/02/25
75/03/27
75/05/06
75/05/22
75/06/26
75/07/17
10 00
10 45
09 00
11 50
09 00
09 00
09 00
09 30
09 00
09 00
11 45
1.680
0.720
0.960
1.200
0.080
0.940
0.600
2.300
2.700
5.600
11EPALES
21412T4
, 0000 FEET JtPTi- CLASS UO
00625
TOT KJEL
N
MG/L
0.795
2.000
.COOK
.700
.OOOK
.000
.600
0.770
1.500
3.100
0.4?0
00610
NH3-N
TOTAL
MG/L
0.035
0.050K
0.050K
0.050K
O.OSOiv
0.140
0.086
0.058
0.050K
0.450
0.025K
00671
PH05-DIS
ORTHO
MG/L P
0.310
2.500
• 0.230
0.257
0.490
0.455
0.180
0.295
0.720
0.840
00665
PHOS-TOT
MG/L P
0.450
2.500
0.430
0.380
0.730
0.870
0.670
1.700
0.460
1.100
0.870
50051
FLOW
RATE
INST MGO
0.105
0.060
0.105
0.100
0.074
0.050
0.050
0.050
0.050
0.040
0.070
50053
CONDUIT
FLOW-MOD
MONTHLY
0.014
0.11C
0.013
0.030
0.100
0.050
0.050
0.090
0.050
0.050
0.050
K VALUE KNOWN TO BE
LESS THAN INDICATED
------- |