Unitsct StatJs
t:tfli."srs! Guidahnas Division
WH-S52
Was.'iinqton DC 20460
fc'PA 440/1 32/302
Ju'y 1982
naqain*nt
EPA
Fate of Priority Pollutants
in Publicly Owned Treatment
Works
30 Day Study
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EPA 440/1-82/302
Fate of Priority Toxic
Pollutants in
Publicly Owned
Treatment Works
30-Day Study
prepared by
E.C. Jordan Co.
562 Congress Street
Portland, Maine 04112
prepared for
U.S. Environmental Protection Agency
Effluent Guidelines Division
EPA Project Officer
Robert M. Southworth, P.E.
August 1982
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DISCLAIMER
This report has been reviewed by the Effluent Guidelines Division, U.S. Envi-
ronmental Protection Agency, and approved for publication. Approval does not
signify that the contents necessarily reflect the views and policies of the
U.S. Environmental Protection Agency, nor does mention of trade names or
commercial products constitute endorsement or recommendation for use.
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ABSTRACT
This project was initiated to document the priority toxic pollutant
variability of the influent waste stream to a Publicly Owned Treatment Works
(POTW) for 30 consecutive days and to determine the fate of these pollutants in
a POTW.
Influent, primary effluent, secondary effluent, primary sludge, secondary
sludge, vacuum filter filtrate, digester decant, and background tap water
samples were collected at a conventional activated sludge plant. Samples were
analyzed for specified conventional and non-conventional pollutants and for
priority toxic pollutants. Results from the 30-day study were compared to
those obtained during a similar six-day sampling program conducted at the same
POTW during another EPA study. With the exception of methylene chloride,
cyanide, and bis(2-ethlyhexyl)phthalate, the variability of the influent
pollutant concentrations for the six-day and the 30-day studies was comparable.
A comparison of the -six-day and 30-day study data reveals that fewer pollutants
were detected 100 percent of the time in the waste streams' during the 30-day
study and that more pollutants were identified at least once during the 30-day
study than during the six-day study. These two factors result from the in-
creased time span of the 30-day study and the diversified industrial character
of the tributary area, respectively, and are consistent for each of the waste
streams sampled.
Combined, the two studies provided a 36-day data base. In the influent
samples, 72 priority toxic pollutants were detected at least once, 24 pollu-
tants were detected at least 50 percent of the time, and seven pollutants were
detected 100 percent of the time. In the secondary effluent waste stream, 53
priority toxic pollutants were detected at least once, 1? priority toxic
pollutants were detected at least 50 percent of the time or greater, and five
pollutants were detected 100 percent of the time. Correlations relating
influent and effluent priority pollutant concentrations were established.
Though consistent statistical relationships do not exist, an increase in the
influent -concentration • was observed to cause a corresponding increase (to a
lesser extent) in the effluent concentration. Results of regression analyses
for the 19 most frequently occurring priority toxic pollutants in the secondary
effluent and several conventional pollutants indicate poor correlations overall.
Daily influent priority toxic pollutant mass loadings revealed that
weekday loadings were substantially greater than weekend loadings. A compari-
son of the average weekday loadings to the average Sunday loadings seems to
confirm the theory that priority toxic pollutants are principally byproducts of
industrial processes. Conservative estimates indicated that a minimum of 70
percent of the metal mass loadings, 76 percent of the base/neutral extractable
organic loadings, 54 percent of the volatile organics loading, and 30 percent
of the acid extractable organic mass loadings are associated with industrial
discharges.
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The calculated average mass removals through secondary treatment were: 74
percent for metals, 80 percent for the volatile organic compounds, 69 percent
for the acid extractable organic compounds, and 62 percent for the base/neutral
extractable organic compounds. The majority of the treatment reduction observed
resulted from the secondary treatment process. The metals and high molecular
weight base/neutral extractable organic compounds tended to concentrate in the
primary and secondary sludges. The volatile organics were substantially
reduced by the activated sludge treatment process, most likely through air
stripping or, to a lesser extent, biodegradation.
Priority toxic pollutant metal influent mass loading (particularly lead,
zinc, mercury, and copper) substantially increased during wet weather periods.
This increase is theorized to be either a result of the pollutants being
present in sediments scoured from the combined sewer collection system or
contained in runoff entering the collection system.
This report was submitted in fulfillment of Contract No. 68-01-5772 by the
E.G. Jordan Company under the sponsorship of the U.S. Environmental Protection
Agency. This report covers the period from September 8, 1980 to October 8,
1981. Work was completed as of May 1, 1982.
-iii-
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CONTENTS
ABSTRACT ii
FIGURES v
TABLES vi
ABBREVIATIONS AND SYMBOLS . . . . viii
ACKNOWLEDGEMENTS ix
1. SUMMARY AND CONCLUSIONS 1
2. INTRODUCTION 5
3. POTW SELECTION AND DESCRIPTION 8
4. SAMPLING PROGRAM 20
^Sample'Locations 20
Sampling Schedule and Procedures 22
Quality Assurance/Quality Control
Sampling Program 24
Operating Factors Affecting Sampling .... 29
5. DISCUSSION OF ANALYTICAL RESULTS 31
Background Pollutant Levels 31
Percent Occurrence Analysis 31
Influent Variability Analysis 42
Estimated Pollutant Loads from
Industrial Sources 46
Treatment Reduction of Priority Toxic
Pollutants 49
Priority Toxic Pollutant Mass
Balance Analysis 65
Correlation of Influent and Effluent Priority
Toxic Pollutant Concentrations 67
Correlation of Effluent Priority Toxic
Pollutant Concentrations to Conventional
Pollutant Concentrations 69
Effects of Combined Sewer Flows During Wet
Weather Periods . 69
Quality Assurance/Quality Control Results. . 75
APPENDICES 79
A. ASBESTOS RESULTS
B. QA/QC DATA
C. DAILY ANALYTICAL RESULTS
D. DAILY MASS BALANCE TABLES
-iv-
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FIGURES
Number Page
1 Flow Schematic of the MBWWTP 14
2 Typical Automatic Sampler Set-up 21
3 Daily Chloroform Mass Loading Graph 48
4 Linear Correlation Graph for Benzene 70
5 Pollutant Loading and Flow During Wet
Weather Periods 74
-v-
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TABLES
Number Page
1 Primary Industrial Categories Identified for
Regulatory Review by EPA 9
2 SIC Codes For Industrial Dischargers to the MBWVTP . . 10
3 Treatment Process Specifications 15
4 Maximum Allowable Influent Concentrations for MBWWTP. . 18
5 Limitations on Wastewater Discharged to the MBWWTP
Sewerage System 19
6 In-Situ Measurements 25
7 Daily Flows for the Six-Day and 30-Day Studies .... 26
8 Sample Schedule and Sampling Techniques 27
9 Summary of Tap Water Analytical Data 32
10 Percent Occurrence of Priority Toxic Pollutants
- 36-Days Combined 33
11 Percent Occurrence of Priority Toxic Pollutants
- 30-Day Study 35
12 Percent Occurrence of Priority Toxic Pollutants
- Six-Day Study 37
13 Comparison of Six-Day, 30-Day and Combined 36-Day
Influent Priority Toxic Pollutant Concentrations . 40
14 Comparison of Six-Day, 30-Day and Combined 36-Day
Secondary Effluent Priority Toxic Pollutant
Concentrations 42
15 Influent Variability Analysis 45
16 Day of the Week Average Influent Pollutant
Loads for the MBWWTP 47
-VI-
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TABLES (cont.)
Number Page
17 Summary of Analytical Data
- 36-Days Combined 50
18 Summary of Analytical Data
- 30-Day Study 55
19 Summary of Analytical Data
- Six-Day Study 60
20 Selected Pollutant Mass Percent Removals 64
21 Mass Balance Analysis for Combined 36-Day Data .... 66
22 Correlation of Influent and Effluent Priority Toxic
Pollutant Concentrations 68
23 Correlation of Secondary Effluent Priority
Pollutant Concentrations to Secondary
Effluent BOD5 and TSS Concentrations 71
24 Influent POTW Metal Loads During
Storm Events 73
-vii-
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LIST OF ABBREVIATIONS AND SYMBOLS
BADT
BATEA
BPT
BOD5
COD
cfm
CSO
CuSO.
4
DL
EPA
EGD-OAS
gpm
HgCL2
HN03
HP
H3P°4
H2S°4
I or J
L, <
mgd
mg/1
ml
MBWWTP
NaOH
NC
ND
ng/1
NS
NSPS
0&.G
PNA
POTV
ppb
QA/QC
sf
SIC
T
TOC
TSS
U
Vg/*
VOA
WAS
best available demonstrated technology
best available treatment economically
achievable
best practicable treatment
biochemical oxygen demand
chemical oxygen demand
cubic foot per minute
combined sewer overflow
copper sulfate
detection limit
U.S. Environmental Protection Agency
Effluent Guideline Division -
Office of Analytical Support
gallons per day
gallons per minute
mercuric chloride
nitric acid
horsepower
phosphoric acid
sulfuric acid
interference present
less than
millions gallons per day
milligrams per liter
milliliter
Mocassin Bend Wastewater Treatment Plant
sodium hydroxide
not calculated
not detected
nanograms per liter
not sampled
aew source,performance standard
oil and grease
polynuclear aromatic hydrocarbons
publicly owned treatment works
parts per billion
quality assurance/quality control
square foot
standard industrial classification
trace
total organic carbon
total suspended solids
unconfirmed
micrograms per Ir.ter
volatile organic analyte
waste activated sludge
-viii-
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ACKNOWLEDGMENTS
This report was conducted under contract to the U.S. Environmental Protec-
tion Agency. The cooperation and efforts of Jeffrey D. Denit, Acting Division
Director, Effluent Guidelines Division (EGD); Harold B. Coughlin, EGD Branch
Chief; and Thomas P. O'Farrell, Project Manager, Office of Water Regulations
and Standards are appreciated. Special recognition is given to the EGD Project
Officer, Robert M. Southworth, P.E., for his efforts in providing direction and
input throughout this study. Acknowledgment is given to Joan Fisk, formerly of
the EGD-Office of Analytical Support, for assisting in the development and
evaluation of the quality assurance/quality control program.
The Jordan Company also wishes to thank the personnel at the Moccasin Bend
Wastewater Treatment Plant, in particular Eugene G. Wright, Superintendent and
George E. Kurz, Staff Engineer, for their unlimited cooperation during this
proj ect.
This report was prepared by Mike A. Crawford, P.E., Project Engineer under
the direction of Donald R. Cote, P.E., Principal-in-Charge; Willard C. Warren,
P.E., Project Manager; and Robert A. Steeves, Technical Project Director. The
E.G. Jordan Company wishes to thank the project staff members for their many
contributions throughout the project, especially during the sampling phase of
the program. Recognition is given to Dave Dionne, Jonathan Freese, Chuck
Goodwin, Mike Murphy, Jim Pendergast, Dave Pineo and Dave Soper. Technical
contributions during the report preparation were made by Robert Steeves, Jim
Pendergast and Deborah Luciano.
-ix-
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SECTION 1
SUMMARY AND CONCLUSIONS
SUMMARY
Influent, primary effluent, secondary effluent, primary sludge and waste
activated sludge streams at the Moccasin Bend Wastewater Treatment Plant
(MBWWTP) in Chattanooga, Tennessee, were flow monitored and sampled for speci-
fied conventional and non-conventional pollutants and for priority toxic
pollutants. Samples were composited each 24-hour period for 30 consecutive
days. Analytical results from the 30-day sampling episode were combined with
analytical results from a six-day sampling episode conducted at the MBWWTP six
months prior to this study to obtain a 36-day data base. Results of the
combined 36-day sampling episode are:
1. A total of 72 priority toxic pollutants were detected in the influent
waste stream at least once during the 36-day combined study; 24 pollutants
were detected 50 percent or more of the time; and seven pollutants were
detected 100 percent of the time. Cyanide1 (883 ug/fc), zinc (358 ug/£),
toluene (329 Vg/£), phenol (244 vg/£), and chromium (226 vg/£) were
present in the influent in the highest average concentrations.
2. A total of 53 priority toxic pollutants were detected in the secondary
effluent at least once during the 36-day combined study; 19 pollutants
were detected 50 percent or more of the time; and five pollutants were
detected 100 percent of the time. Zinc .(99 ug/£), cyanide (92 ug/£),
methylene chloride (72 vg/£), toluene (54 pg/£), nickel (46 ug/£), and
phenol (37 ug/£) were present in the secondary effluent in the highest
average concentrations.
3. A total of 59 priority toxic pollutants were detected in the primary
sludge waste stream at least once during the 36-day combined study; 27
pollutants were detected 50 percent of the time or more; and eight pol-
lutants (chromium, copper, nickel, arsenic, lead, silver, zinc, and
cyanide) were detected 100 percent of the time. Zinc (26.7 mg/£), chro-
mium (13.2 mg/£), cyanide (8.1 mg/£), copper (7.4 mg/£), lead (5.8 mg/£),
nickel (4.1 mg/£), bis(2-ethylhexyl)phthalate (1.5 mg/£), and 1,2,4-
trichlorobenzene (1.1 mg/£) were present in the primary sludge in the
highest average concentrations.
4. A total of 42 priority toxic pollutants were detected in the secondary
sludge at least once during the 36-day combined study; 14 pollutants were
detected 50 percent or more of the time; and seven priority toxic pollu-
tants (chromium, copper, silver, zinc, nickel, arsenic, and cyanide) were
Combined 36-day average includes analytical results from the six-day
study which are suspected to be erroneously high.
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detected 100 percent of the time. Chromium (5.5 rag/£), copper (1.2 mg/Z),
lead (0.7 rag/fc), nickel (0.7 mg/fc), cyanide (0.6 mg/fc), bis(2-ethylhexyl)
phthalate (0.2 mg/£), and silver (0.2 mg/£) were present in the secondary
sludge in the highest average concentrations.
5. Chloroform was detected at an average concentration of 74 ug/fc in the
influent waste stream throughout the 36-day sampling period. This pol-
lutant was also detected in 100 percent of the municipal tap water samples
at an average concentation of 32 ug/fc.
6. For those priority toxic pollutants detected in the influent waste stream
during the 36-day combined study over 50 percent of the time, average
secondary treatment mass removals through biological treatment were 74
percent for metals, 80 percent for volatile organic compounds, 69 percent
for acid extractable organic compounds, and 62 percent for the base/neutral
extractable organic compounds.
7. The average percent removal for the combined 36-day study for both bio-
chemical oxygen demand (BODS) and total suspended solids (TSS) through
biological treatment was 86 percent.
8. Quality assurance results for the 30-day data indicate that the wastewater
data are good overall. The average of mean recoveries was 89.5 ± 16.8 percent
for purgeable compounds; 79 ± 18.5 percent for base/neutral pollutants;
45.0 ± 23.9 percent for acid pollutants (phenol being the only commonly
occurring acid pollutant); and greater than 95 percent for metals (except
for boron and tin which had low recoveries overall).
9. Quality assurance results for sludge samples were fair overall in compari-
son to the wastewater quality assurance data. The average of mean recoveries
was 100.49 ± 15.5 percent for purgeable compounds; 45.0 ± 23.4 percent
for base/neutral compounds; 36.6 ± 17.9 percent for acid compounds; and
74.0 ±47.1 percent for metals.
The 30-day study provides a long-term data base that identifies the
occurrence, quantity and fate of priority toxic pollutants as the pollutants
travel through a POTW. As a result of the established data base prior to the
implementation of a pretreatment program, the MBWWTP provides an excellent
facility for further priority toxic pollutant studies. The effects on the
influent quality for the POTW after enforcement of a pretreatment program
should be addressed in a subsequent study.
CONCLUSIONS
The following conclusions are based on results of evaluation of the
six-day, 30-day, and combined 36-day data:
1. Forty-three percent of the chloroform in the influent waste stream to the
MBWWTP is attributable to the chloroform in the potable water supply of
the Chattanooga area.
2. With the exception of cyanide, the influent priority pollutant concentra-
tions from the six-day and 30-day studies are comparable. All but five
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pollutant mean values from the six-day study are within one standard
deviation of the mean values from the 30-day study. The influent data
from the six-day study adequately represents daily influent loads to the
MBWWTP.
3. The bulk of the priority pollutants in the influent waste stream to the
MBWWTP appear to originate as byproducts of industrial processes.
4. Primary sedimentation did not afford significant toxic pollutant removals.
Primary treatment removals for toxic pollutants ranged from less than 20
percent for metals and volatile organics to no removal for acid fractions.
Several base/neutral pollutants exhibited an affinity to concentrate in
the primary sludge; however, net primary removals were low due to the
presence of these pollutants at such low concentrations (near the pollutant
detection limit) in the influent and primary effluent waste streams.
Total suspended solids removal averaged only 30 percent (design removal is
60 percent).
5. The majority of treatment reduction was the result of the activated sludge
secondary treatment process. Volatile organic compounds were signifi-
cantly air-stripped or biodegraded during secondary treatment as evidenced
by the decrease in volatile organic concentrations across the activated
sludge process and lack of pollutant accumulation in the WAS. Bio-floe
adsorption was the primary removal mechanism for acid, base/neutral, and
metal compounds as indicated by the increase in pollutant concentrations
in the WAS.
6. Results of mass balance analyses indicate that acid, base/neutral and
volatile compounds are reduced significantly during secondary treatment.
Metal compounds showed a dramatic increase across the secondary system.
Erroneous WAS pump records are suspected as causing this mass increase of
conservative pollutants.
7. The vacuum filter filtrate and digester decant waste streams, although
high in metal content, are insignificant in the overall metals mass
balance due to the low volumes of these recycle lines.
8. Correlations relating influent and effluent priority toxic pollutant
concentrations indicate changes in the influent concentration do affect
the effluent concentrations. In general, slopes of the linear correla-
tions were greater than one, indicating that an increase in the influent
concentration results in a corresponding increase (to a lesser extent) in
the effluent concentration.
9. Regression analyses between the 19 most freqently occurring priority
toxic pollutants in the secondary effluent and two conventional pollutants
(BODJ5 and TSS) showed poor correlations. In general, the level of BOD5 or
TSS is not indicative of the level of toxic pollutants in the secondary
effluent.
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10. Influent loads (particularly for lead, zinc and copper) increased substan-
tially during three separate storm events. This appears to result either
from metals entering the sewerage system in urban runoff via combined
sewers or from sewer sediments being scoured from the collection system
during storm events.
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SECTION 2
INTRODUCTION
BACKGROUND
Prior to 1972, efforts to curb the pollution of the nation's waterways
were directed mainly toward controlling conventional pollutants: total sus-
pended solids (TSS), biochemical oxygen demand (BOD5), viruses and bacteria
(indicated by coliform count), and acidity or alkalinity (pH). These para-
meters were regulated on a case by case basis for direct dischargers, taking
into account the assimilative capacity of the stream receiving the treated
effluents. In 1972, the Water Pollution Control Act Amendments (P.L.92-500)
were enacted and a wholly different approach to regulating pollutant discharges
was initiated.
P.L. 92-500 required the U.S. Environmental Protection Agency (EPA) to
promulgate national technology-based effluent limitations for both municipal
and industrial dischargers. The limitations were to be based on the perform-
ance of a selected wastewater treatment technology considering factors such as
costs and non-water quality environmental impacts. P.L. 92-500 required that
the municipal limitations be uniformly applied to all municipal dischargers and
that the industrial limitations be uniformly applied to industries in the same
category or subcategory.
Two levels of control were required for existing industrial dischargers in
P.L. 92-500: 1) limitations based on Best Practicable Technology (BPT) (to be
met by 1977); and 2) limitations based on Best Available Technology Economically
Achievable (BAT or BATEA), a more stringent level of control with a compliance
date of mid-1983. The Act also required EPA to promulgate New Source Perform-
ance Standards (NSPS) based on the Best Available Demonstrated Technology
(BADT). NSPS applied to industrial facilities constructed after promulgation
of the standards.
P.L. 92-500 required EPA to develop a list of toxic pollutants and to
establish effluent limitations for these pollutants. Selection of the pollu-
tants to be placed on the list and the respective effluent limitations were to
be based on the effect of a pollutant on the water environment.
Congress also addressed indirect discharges [industries that discharge
their wastewater to a publicly owned treatment works (POTW)] in P.L. 92-500.
EPA was required to promulgate technology-based pretreatment standards for
indirect dischargers for any pollutant that interfered with, passed through, or
was otherwise incompatible with POTWs.
In June 1976, the Natural Resources Defense Council, Inc. (NRDC) brought
legal action against EPA to hasten compliance with certain sections of P.L.
92-500. As a result of a settlement agreement between EPA and NRDC, EPA was
required to promulgate effluent limitations by industrial category for 65 toxic
compounds or classes of compounds which were subsequently divided into 129
priority toxic pollutants. The limitations were to be based on BAT instead of
the water quality considerations specified in P.L. 92-500 for toxic pollutants.
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In 1977, Congress enacted the Clean Water Act (P.L. 95-217). The new Act
included the settlement agreement requirement for BAT limitations for priority
toxic pollutants as well as some new provisions including extending the July
1983 deadline for complying with priority pollutant BAT limitations to July
1984. In addition, P:"L. 95-217 required EPA to promulgate BAT limitations for
other toxic pollutants and for non-conventional pollutants. The Act also
stipulated that effluent limitations for conventional pollutants be based on
Best Conventional Technology (BCT) instead of BAT. The requirement in P.L.
92-500 for NSPS for new direct industrial dischargers and pretreatment stand-
ards for indirect dischargers remained unchanged in the new Act.
In an effort to determine the source, occurrence, and fate of priority
toxic pollutants in sewerage systems and in POTVs, EPA initiated several
related studies. In one study, the sources (residential, commercial, or
industrial) of priority toxic pollutants in the influent to POTVs were evalu-
ated. A second study addressed the occurrence and fate of priority toxic
pollutants in 40 POTWs with different treatment processes and diversified
industrial wastewater contributions; this study was later expanded to include
10 additional POTWs, each with only one significant industrial discharger. The
third study (the subject of this report) evaluated the occurrence and fate of
priority toxic pollutants in a POTW for 30 consecutive days; the influent waste
stream variability for the 30-day period was compared to the variability found
during a previously conducted six-day study. A fourth study is currently being
conducted through the Nationwide Urban Runoff Program to assess the occurrence
of priority toxic pollutants in urban runoff. A fifth study has recently been
initiated to estimate the magnitude of priority toxic pollutants in combined
sewer flows and in combined sewer overflows.
Collectively, these studies provide much information on the source,
occurrence, and fate of priority toxic pollutants in sewerage systems and in
POTWs. This 30-day study serves to fill the informational void regarding the
long-term variability of priority toxic pollutants in POTWs.
PURPOSE
The purposes of the 30-day study are: 1) to compare the variability of
POTW influent priority toxic pollutant concentrations for a six-day and 30-day
sampling episode; 2) to document the amount of priority toxic pollutants
discharged to a POTW before full implementation of a local pretreatment pro-
gram; 3) to evaluate the performance of POTW processes with respect to treatment
of priority toxic pollutants; and 4) to document the fate of priority pollutants
in a POTW.
SCOPE OF WORK
This study involved five major tasks:
1. selecting a representative POTW to sample;
2. sampling various wastewater streams at the selected POTW for 30
consecutive days;
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3. analyzing the collected samples for priority toxic pollutants and for
specified conventional and non-conventional pollutants;
4. inputing the sample analytical results to a computerized data base;
and
5. evaluating the data and preparing a final report.
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SECTION 3
POTW SELECTION AND DESCRIPTION
POTW SELECTION
Criteria used to select the POTW for the 30-day study were similar to
those used in selecting the 50 POTWs for EPA's "Fate of Priority Toxic Pollu-
tants in POTWs" study. Selection was based on:
o type of treatment process;
o size of the treatment plant;
o amount and type of industrial wastewater contribution;
o efficiency of the treatment plant;
o flow in relation to design capacity; and
o geographical location.
Another consideration in selecting the POTW for the 30-day study was that
it be one of the POTWs sampled during the 50 POTW study; data resulting from
the six-day sampling episode for the 50 POTW study could then be combined with
data obtained from the 30-day study to provide an expanded data base for the
variability analysis. The POTW selected had to be operating under the same
conditions when the 30-day study was initiated as it was during the sampling
episode for the 50 POTW study.
The Moccasin Bend Wastewater Treatement Plant (MBWWTP) in Chattanooga,
Tennessee satisfied all selection criteria and was chosen for the 30-day study.
The MBWWTP receives a substantial and diversified industrial flow; employs the
activated sludge treatment process, one of the most common biological treatment
processes currently used at POTWs; operates at a high BOD5_ and TSS removal
efficiency; and has a high actual flow as a percentage of design capacity. In
addition, samples could easily be shipped from the MBWWTP to the laboratory
daily.
POTW DESCRIPTION
The Moccasin Bend Wastewater Treatment Plant (MBWWTP) is a 42 ragd (average
design flow) conventional activated sludge treatment plant that treats an
average dry weather flow of 42 mgd. Approximately 50 percent of the dry
weather flow, 65 percent of the biochemical oxygen demand (BOD5), and 75 per-
cent of the chemical oxygen demand (COD) originates in the industrial sector.1
Industries in 21 of the 37 primary industrial categories (see Table 1)
identified for regulatory review by the EPA discharge to Chattanooga's municipal
sewerage system (133 permitted industrial dischargers with 174 outfalls).
Table 2 lists the standard industrial classification (SIC) codes for the indus-
Information provided by MBWWTP personnel,
8
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TABLE 1. PRIMARY INDUSTRIAL CATEGORIES IDENTIFIED FOR REGULATORY REVIEW BY EPA+
Adhesives and Sealants
Aluminum Forming
Auto and Other Laundries *
Battery Manufacturing
Coal Mining
Coil Coating
Copper Forming *
Electrical and Electronic Components *
Explosives Manufacturing
Foundries *
Gum and Wood Chemicals
Ink Formulating
Inorganic Chemicals Manufacturing *
Iron and Steel Manufacturing *
Leather Tanning and Finishing *
Metal Finishing*
Nonferrous Metals Manufacturing *
Nonferrous Metal Forming*
Ore Mining and Dressing
2
Organic/Plastics*
Paint Formulation *
Paving and Roofing Materials
Pesticides
Petroleum Refining *
Pharmaceutical Manufacturing*
Photographic Equipment and Supplies
Plastics Processing
Plastics Molding and Forming
Porcelain Enameling *
Printing and Publishing *
Pulp, Paper, and Paperboard*
Rubber Manufacturing*
Shipbuilding
Soap and Detergent Manufacturing *
Steam Electric Power Plants
Textile Mills *
Timber Products Processing *
+ As of August 7, 1981
* Industries in this category discharge to the MBWWTP
1 The Electroplating and the Mechanical Products Categories have been
combined under the Metal Finishing Category.
2 The Organic Chemicals and the Plastics and Synthetics Categories have
been combined under the Organic/Plastics Category.
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TABLE 2. SIC CODES FOR INDUSTRIAL DISCHARGERS TO THE MBWWTP
SIC CODE*
2013(1)
2016(2)
2026(3)
2037(1)
2041(2)
2051(3)
2052(3)
2086(2)
2087(1)
2251(1)
2252(4)
2253(1)
2254(1)
2258(1)
2261(2)
2262(3)
2269(2)
2272(2)
2281(3)
2491(1)
2611(1)
2631(2)
2653(2)
2751(1)
2752(5)
2813(1)
2819(1)
2822(2)
2833(3)
2834(2)
2841(1)
2843(1)
2851(1)
2865(1)
2869(3)
2952(1)
3069(1)
SIC DESCRIPTION
Sausages & other prepared meat products
Poultry dressing plants
Fluid milk
Frozen fruits, fruit juices and vegetables
Flour and other grain mill products
Bread and other bakery products, except cookies and crackers
Cookies and crackers
Bottled and canned soft drinks and carbonated waters
Flavoring extracts and flavoring syrups, not elsewhere classified
Women's full-length and knee-length hosiery
Hosiery, except women's full-length and knee-length hosiery
Knit outerwear mills
Knit underwear mills
Warp knit fabric mills
Finishers of broad woven fabrics of cotton
Finishers of broad woven fabrics of man-made fiber and silk
Finishers of textiles, not elsewhere classified
Tufted carpets and rugs
Yarn spinning mills: cotton, man-made fibers and silk
Wood preserving
Pulp mills
Paperboard mills
Corrugated and solid fiber boxes
Commercial printing,
Commercial printing,
Industrial gases
Industrial inorganic chemicals, not elsewhere classified
Synthetic rubber (vulcanizable elastomers)
Medicinal chemicals and botonical products
Pharmaceutical preparations
Soap and other detergents, except specialty cleaners
Surface active agents, finishing agents, sulfonated oils
Paints, varnishes, lacquers, enamels, and allied products and
assistants
Cyclic (coal tar) crudes, and cyclic
intermediates, dyes, and organic pigments (lakes and toners)
Industrial organic chemicals, not elsewhere classified
Asphalt felts and coatings
Fabricated rubber products, not elsewhere classified
letterpress and screen
lithographic
* Number in parentheses indicates the number of dischargers that have this
SIC code as their primary activity.
10
-------
TABLE 2 (cont.)
SIC CODE* SIC DESCRIPTION
3111(1) Leather tanning and finishing
3199(1) Leather goods, not elsewhere classified
3221(2) Glass containers
3264(4) Porcelain electrical supplies
3312(1) Blast furnaces (including coke ovens), steel works and rolling
mills
3321(8) Gray iron foundries
3429(1) Hardware, not elsewhere classified
3433(1) Heating equipment, except electrical and warm air furnaces
3443(13) Fabricated plate works (boiler shops)
3462(1) Iron and steel forgings
3469(1) Metal stampings, not elsewhere classified
3471(6) Electroplating, plating, polishing, anodizing and coloring
3494(1) Valves and pipe fitting, except plumbers brass goods
3496(1) Miscellaneous fabricated wire products
3523(4) Farm machinery and equipment
3531(1) Construction machinery and equipment
3552(1) Textile machinery
3581(2) Automatic merchandising machines
3631(1) Household cooking equipment
3634(1) Electric housewares and fans
3639(1) Household appliances, not elsewhere classified
3662(1) Radios and television transmitting, signaling, and detection
equipment
3713(1) Trucks and bus bodies
3911(1) Jewelry, precious metal
3949(3) Sporting and athletic goods, not elsewhere classified
4011(2) Railroads, line-haul operating
4013(1) Switching and terminal establishments
4231(1) Terminal and joint terminal maintenance facilities for motor
freight transportation
4941(1) Water supply
4961(1) Steam supply
5082(1) Construction and mining machinery and equipment
5085(1) Industrial supplies
5144(1) Poultry and poultry products
5161(2) Chemicals and allied products
7211(1) Power laundries, family and commercial
7213(5) Linen supply
7214(1) Diaper service
7218(1) Industrial launderers
* Number in parentheses indicates the number of dischargers that have this SIC
code as their primary activity.
11
-------
TABLE 2 (cont.)
SIC CODE* SIC DESCRIPTION
7391(1) Research and development laboratories
7395(7) Photofinishing laboratories
7513(1) Truck rental and leasing, without drivers
7538(1) General automotive repair shops
7542(9) Car washes
7694(1) Armature rewinding shops
7699(1) Repair shops and related services, not elsewhere classified
* Number in parentheses indicates the number of dischargers that
have this SIC code as their primary activity.
12
-------
trial dischargers to the MBWWTP. Seasonal variations in the flow and organic
loadings for this plant are not significant.
The MBWWTP is served by a collection system that was substantially com-
plete by 1930. Approximately seven percent of the system consists of combined
sewers, with the oldest dating back to the turn of the century. Many of these
original conduits have been replaced or rehabilitated. The original larger
conduits were egg-shaped brick sewers; smaller ones were made of clay pipe with
mortar joints. Beginning in 1969, many of the brick sewers were lined with
pneumatically applied concrete to revitalize and seal the deteriorating lines
and reduce extraneous water that entered the system as infiltration.
Until the interceptor system and pumping stations went into operation in
1959, all sewage was discharged directly (without treatment) to the Tennessee
River and South Chicamauga Creek. In 1962, the primary plant (grit chamber,
primary settling tanks, anaerobic digesters, filter building) went on line. In
1972, the secondary treatment portion of the existing system began operation.
Wastewater flowing into the treatment plant is initially screened (bar
screens), pumped to a grit chamber, and passed through a comminutor. Primary
sedimentation, diffused aeration, secondary clarification, and chlorination
follow. Wastewater is then discharged to the Tennessee River. Because of
excessive inflow during wet weather conditions (attributable in part to the
remaining combined sewers), a bypass around the treatment plant can be utilized
if flows are in excess of peak design flow. The plant has magnetic influent
and waste activated sludge flow meters and a Venturi effluent flow meter.
Primary sludge is anaerobically digested, vacuum filtered, and trucked to
an approved landfill. When the plant was upgraded in 1971, a wet-air oxidation
unit was constructed to treat the secondary waste activated sludge, but it is
not currently operating. The waste activated sludge is presently discharged
directly to the Tennessee River under an interim National Pollutant Discharge
Elimination System (NPDES) permit. Digester decant, vacuum filter filtrate,
and a scum return line are recirculated to the plant directly upstream of the
bar screens. Figure 1 presents a flow schematic of the current treatment
process; Table 3 lists the treatment processes' design specifications.
The MBWWTP authority recently initiated an $83 million facility expansion,
scheduled for completion in January 1984. As part of this expansion, the
existing aeration tanks will be converted to a pure oxygen system; the primary
and secondary sedimentation capacity will be increased; and sludge treatment
processes will be upgraded.
The pretreatment program in Chattanooga has evolved over the years begin-
ning in January 1977. At that time, the City Commission adopted an ordinance
that established pretreatment standards for 32 different pollutants. These
standards were based on effluent limitations for direct dischargers as imposed
by the State of Tennessee under its own permit system.
The MBWWTP staff later evaluated the standards with respect to the require-
ments of Section 307 of the Clean Water Act which prohibit the discharge of
pollutants that are incompatible with POTWs. As a result of this evaluation,
13
-------
SLUDGE TO LANDFILL
EFFLUENT
TO .
RIVES
(BYPASS)
SAMPLE LOCATION
FIGURE 1. FLOW SCHEMATIC OF THE MOCCASIN BEND WASTEWATER TREATMENT PLANT
-------
TABLE 3. TREATMENT PROCESS SPECIFICATIONS
I. Bar Screens
Mechanically cleaned
Bar screen opening: one inch
II. Raw Waste Pumping Station
3 pumps, each rated at 40 mgd
Average design flow: 40 mgd
Peak flow: 120 mgd
III. Grit Removal
Detritor unit (or constant level sedimentation tank) rated at 60 mgd
Aerated grit chamber rated at 90 mgd (not currently operational)
Grit chamber dimensions: 36-feet x 24-feet x 13.5-feet deep
IV. Comminutors
5 comminutors, each rated at 20 mgd
Solids size: 3/8 inch maximum
V. Primary Settling Tanks
4 primary settling tanks
Average design surface settling rate: 1,600 gpd/sf
Average design detention time: 1 hour (total)
Average design BOD5_ removal: 10 percent
Average design TSS removal: 60 percent
Average design suspended solids removal: 60,000 pounds/day (total)
Settling tank dimensions, (each): 131-feet x 50-feet x 9-feet deep
Total volume: 235,800 cf
VI. Aeration Basin
4 aeration tanks with 4 passes each
MLSS = 2,500 mg/£
6 blowers, each rated at 500 HP, 12,800 cfm
5 blowers continuously operating, 1 standby
Average detention time: 5 hours (total)
3 variable speed return sludge pumps, each 1,825 to 3,650 gpm
Aeration tank dimensions (each tank): 120-feet x 237-feet x 15-feet deep
15
-------
TABLE 3 (cont.)
VII. Secondary Clarifiers
8 secondary settling tanks
Average design surface settling rate = 750 gpd/sf
Detention time =2.5 hours (total)
Settling tank dimensions (each): 175-feet x 40-feet x 10.5-feet deep
Total volume: 588,000 cf
VIII. Disinfection
2 chlorine contact tanks, each with 3 passes
Average detention time = 29 minutes (total) at 42 mgd
Contact tank dimensions (each): 140-feet x 35-feet x 11.5-feet deep
IX. -Anaerobic Digester
6 tanks - 3 primary digesters/3 secondary digesters
Average detention time = 30 days (total)
Methane gas production = 15 cf/lb of volatile matter = 300,000 cf/day
Digester dimensions: 65 feet in diameter x 20 feet deep
X. Sludge Dewatering
4 vacuum filters
Design capacity =3.5 Ib/sf/hour
Quantity of sludge produced: 408 dry tons/year (total)
Approximately 220 Ib/day of polymer is used
Filter dimensions (each): 8-feet diameter x 10-feet long
16
-------
two important criteria were developed: critical protection concentrations for a
particular pollutant entering the treatment plant and the concentration of a
pollutant discharged to the sewerage system.
By comparing the influent concentration to the critical protection crite-
ria mentioned above, the MBWWTP staff is able to routinely identify if any
pollutants are close to impacting the treatment process. The MBWWTP industrial
pretreatment -staff monitors industrial discharges annually and requires periodic
self monitoring reports which vary from weekly to annually depending on the
discharger. A current inventory of the industrial dischargers and the charac-
teristics of their waste stream are maintained by means of a computer program.
The monitoring program, in conjunction with the established computer pollutant
mass inventory, provides the MBWWTP staff with a current mass balance for the
collection system. Once a pollutant is determined to be approaching the
critical influent concentration at the treatment plant, the staff evaluates
the sources of the pollutant and initiates controls for the discharge of the
pollutant to the collection system.
The City imposed two requirements when the pretreatment standard was
established in 1977. The first requirement was to regulate all pollutants, by
January 1, 1981, that exceed the critical influent concentrations. Table 4
summarizes the current maximum allowable pollutant concentration in the influ-
ent. Under the second requirement, industrial dischargers were to meet the EPA
and State approved limitations listed in Table 5 by January 1, 1983. In
addition to these limitations, the discharge of the following pollutants to the
sewerage system was prohibited:
(1) Pollutants that create a fire or explosion hazard in the POTW;
(2) Pollutants that cause corrosive structural damage to the POTW, but in
no case discharges with a pH lower than 5.0 or higher than 10.5;
(3) Solid or viscous pollutants in amounts that cause obstruction to the
flow of the sewers, or other interference with the operation of or
that cause injury to the POTW, including waxy or other materials that
tend to coat and close a sewer line or other appurtenances thereto;
(A) Any pollutant, including oxygen demanding pollutants (e.g., BOD5),
released in a discharge of such volume or strength as to cause
interference in the POTW;
(5) Heat in amounts that inhibit biological activity in the POTW result-
ing in interference, but in no case'heat in such quantities that the
temperature at the treatment works influent exceeds 40° Centigrade
(104° Fahrenheit). Unless a higher temperature is allowed in the
user's wastewater discharge permit, no user shall discharge into any
sewer line or other appurtenane of the POTW wastewater with a tempera-
ture exceeding 65.5° Centigrade (150° Fahrenheit).
17
-------
TABLE 4. MAXIMUM ALLOWABLE INFLUENT CONCENTRATIONS FOR MBWWTP
Criteria to Protect the Treatment Plant Influent:
The Superintendent shall monitor the treatment works influent for each
parameter in the following table. The-Industrial Users shall be subject to the
reporting and monitoring requirements set forth in Section 32-48 and Section
32-49 as to these parameters. In the event that the influent at the treatment
works reaches or exceeds the levels established by said table, the Superinten-
dent shall initiate technical studies to determine the cause of the influent
violation, and shall recommend to the Board such remedial measures as are
necessary, including but not limited to recommending the establishment of new
or revised pretreatment levels for these parameters. The Superintendent shall
also recommend changes to any of these critera in the event the POTW effluent
standards are changed or in the event that there are changes in any appliable
law or regulation affecting same or in the event changes are needed for more
effective operation of the POTW.
Parameter
Maximum
Concentration
mg/l(24 Hour Flow-
Proportional
Composite Sample)
Maximum
Ins t ant aneous
Concentration
mg/l(Grab Sample)
Antimony (Sb)
Arsenic (As)
Cadmium (Cd)
Chromium-
total (Cr
Chromium-
Hexavalent (Cr+6)
Copper (Cu)
Cyanide (CN)
Iron (Fe)
Lead (Pb)
Manganese (Mn)
Mercury (Hg)
Nickel (Ni)
Phenols
Selenium (Se)
Silver (Ag)
Zinc (Zn)
Total Dissolved Solids
Biochemical Oxygen Demand
Suspended Solids
Ammonia Nitrogen
PH
1.0
0.05
0.01
1.7
0.5
0.40
0.05
10.0
0.10
0.50
0.05
.75
.00
0.01
0.05
2.00
5000
500
-u
*»
27
0,
1,
2.0
0.1
0.02
3.4
1.0
0.8
0.1
20.0
0.2
1.0
0.1
1.5
2.0
0.02
0.1
4.0
44
6-9
(std.units)
From City of Chattanooga Ordinance No. 7129 (Amended December 1978) pp.
17-18.
* Not to exceed the design capacity of treatment works.
18
-------
TABLE 5. LIMITATIONS ON WASTEWATER DISCHARGED TO
THE MBWWTP SEWERAGE SYSTEM
+Limitations on Vastewater Strength: No person or user shall discharge waste-
water in excess of the concentration set forth in the table below unless: (1)
an exception has been granted the user under the provisions of Section 32-47;
or (2) the wastewater discharge permit of the user provides as a special permit
condition a higher interim concentration level in conjunction with a require-
ment that the user construct a pretreatment facility or institute changes in
operation and maintenance procedures to reduce the concentration of pollutants
to levels not exceeding the standards set forth in the table within a fixed
period of time.
Maximum
Concentration Maximum
rag/1(24 Hour Flow- Instantaneous
Proportional Concentration
Parameter Composite Sample) mg/l(Grab Sample)
Biochemical
Oxygen Demand *
Chemical
Oxygen Demand * -
Suspended Soilids *
Arsenic (As) 1.0 , 2.0
Cadmium (Cd) 1.0 2.0
Chromium-
Total (Cr) 5.0 10.0
Chromium-
Hexavalent (Cr+6) 0.05 0.10
Copper (Cu) 5.0 10.0
Cyanide (CN) 2.0 4.0
Lead (Pb) 1.5 3.0
Mercury (Hg) 0.1 0.2
Nickel (Ni) 5.0 10.0
Selenium (Se) 1.0 2.0
Silver (Ag) 1.0 2.0
Zinc (Zn) 5.0 10.0
Oil & Grease
(Petroleum and/or
Mineral) 100.0 200.0
+ From: City of Chattanooga Ordinance No. 7129 (Amended December 1978) p.16.
* Limited by design capacity
19
-------
SECTION 4
SAMPLING PROGRAM
The 36-day data base evaluated during this study consists of six, six-day
sampling episodes. As part of EPA's 50 POTW study, the first of these episodes
was conducted from 0800 hours on September 15, 1980, through 0800 hours on
September 21, 1980. The remaining five episodes were conducted from 0800 hours
on February 10, 1981, through 0800 hours on March 12, 1981. The influent to
the MBWWTP, the primary effluent, treated effluent [after chlorination and
before the waste activated sludge (WAS) is combined with the treated effluent],
primary sludge, and waste activated sludge waste streams were sampled each day.
Digester decant, vacuum filter filtrate, and tap water were each sampled once
per sampling episode, or six times over the entire program. The flow schematic
in Figure 1 depicts the treatment processes and sample locations. Sample
frequencies, sampling techniques and sample locations were identical for the
six-day and for the 30-day efforts except where this report documents protocol
modifications.
SAMPLE LOCATIONS
Influent
The total influent waste stream was sampled at a manhole situated immedi-
ately upstream of the POTW's digester decant and vacuum filter filtrate return
lines. The invert of the sewer is approximately 35 feet below grade at. this
location and the sewer is steep, providing a well-mixed, turbulent flow.
Because of the depth of the influent manhole, automatic composite sampling was
not possible at this location. Samples were collected and composited manually
every hour during the 30-day study. Samples were composited manually every two
hours during the initial 6-day study. During wet weather conditions, part of
the total influent waste stream is bypassed directly to the Tennessee River.
Primary Effluent
Overflow from the four primary settling tanks was sampled from a rectan-
gular concrete channel common to all four settling tanks, accessible just
upstream from the plant's aeration tank. The samples collected represent
combined, homogenized primary effluent samples. A five-foot length of rigid
conduit was used to secure the automatic sampler tubing so that it faced into
the waste stream. Figure 2 depicts a typical automatic sampler arrangement.
Treated Effluent
The secondary effluent is discharged from two identical parallel secondary
clarifier networks into two parallel chlorine contact tanks. Effluents from
both chlorination units were sampled by automatic samplers. At the end of
each 24-hour period, the two 2.5-gallon composite samples were blended to
produce a single 5-galIon effluent composite. Rigid conduit was used to secure
the sampler tubing so that samples were drawn from the chlorine contact tanks'
effluents-.
20
-------
AUTOMATIC SAMPLER AND
COMPOSITE CONTAINER
TEFLON TUBING
RIGID ALUMINUM CONDUIT
SAMPLER TUBING
FACING INTO WASTE
STREAM AT MID-DEPTH
OF CHANNEL
•FLOW
TYPICAL AUTOMATIC SAMPLER SET-UP
21
-------
Primary Sludge
Primary sludge is collected in a wet-well, then pumped to the anaerobic
digesters once per shift (three times per day) at a rate of approximately
180,000 gallons per day. The amount of sludge pumped to the digesters and the
pumping intervals varies according to the plant's operating conditions.
Because the'sludge has a high total solids concentration and is pumped to the
digesters at varied time intervals, automatic samplers were not used at this
point. Instead, three liters were collected three times per day and were
manually composited. Grab samples for cyanide, oil and grease, total phenol
and VOAs were also taken at this time.
Waste Activated Sludge
Waste activated sludge is withdrawn continuously from each of the two
parallel secondary clarifier units that follow the aeration chamber. The low
solids content of the waste stream (less than two percent) permitted the use of
automatic samplers at both wet-wells. The 2.5-gallon composite samples col-
lected from each clarifier were blended at the end of each 24-hour period to
form a single 5-gallon composite sample. Rigid conduit was secured in the
wet-wells at both locations to hold the sampler tubing in a well-mixed zone.
Digester Decant
During each six-day sampling episode, a single grab sample was collected
from the decant line of the anaerobic digester. The sample was drawn from a
valve on the decant line, which is located in the digester building. To ensure
as representative a sample as possible, the decant line was flushed for several
minutes before the sample was collected.
Vacuum Filter Filtrate
During each six-day sampling episode, a single grab sample was collected
from the filtrate return line. Once the filtrate line had been flushed thor-
oughly, an intermediate vessel was filled with sample from which a sample for
each pollutant fraction was obtained.
Tap Water
Samples of the potable water supplied to the Chattanooga area were pro-
cured from a faucet located in the headworks building at the MBWWTP to deter-
mine background levels of contaminants. Once the tap water line had been
flushed thoroughly, the appropriate sample containers were filled directly from
the faucet. These samples were representative of the chlorinated domestic
water supplied to the city of Chattanooga by the Tennessee American Water
Company.
SAMPLING SCHEDULE AND PROCEDURES
Sample periods for the six-day and thirty-day studies began at 0800 hours
each morning and proceeded until 0800 hours the next morning. Automatic
samplers were used wherever the sampling conditions allowed. All composite
samples, whether procured manually or automatically, represent time-composited
(constant time-constant volume) samples. At the completion of each sample
22
-------
period, composite samples were homogenized, then separated into the following
fractions: priority toxic pollutant extractables (acids, base/neutrals, and
pesticides); metals; chemical oxygen demand (COD), total organic carbon (TOC),
and ammonia as nitrogen (NH -N) fraction; and biochemical oxygen demand (BOD5)
and residue fraction. Volatile organic analytes (VOAs), cyanide (CN), oil and
grease (O&G) and total phenol fractions were all collected as grab samples
every four hours and preserved immediately because of the volatility and/or
instability of these compounds. These grab samples were composited in the
laboratory prior to analysis. All sample fractions were forwarded to the
appropriate laboratories on a daily basis.
Influent samples were taken from the incoming waste stream in a stainless
steel bucket attached to a 40-foot rope. The bucket was routinely rinsed in
the influent waste stream before samples were collected. Composite aliquots of
940 ml were grabbed every two hours during the six-day study; aliquots of 470
ml were taken every hour during the 30-day study. Composite aliquots were
poured from the stainless steel bucket into a calibrated pyrex beaker, then
into a three-gallon composite jug, which was iced constantly. Grab samples for
VOAs, cyanide, O&G, and total phenol were collected every four hours (1200,
1600, 2000, 2400, 0400, and 0800).
Automatically composited samples (extractable organic compounds, metals,
BOD5, COD, TOC, residue, and ammonia) were collected daily at the primary
effluent location. An ISCO model 1590 sampler was programmed to draw 150 ml
every 20 minutes from mid-depth of the concrete channel. Composite samples
were collected in a 2.5-galIon glass container, which was iced constantly at
the sample location. Grab samples for VOAs, cyanide, O&G and total phenol were
collected according to the same sample schedule used at the influent location.
A one liter pyrex beaker attached to a sampling pole was used to collect grab
samples. The beaker was rinsed thoroughly in the waste stream before being
filled with sample.
At both the treated effluent and waste activated sludge locations, two
ISCO model 1590 samplers were programmed to draw 135 ml each every 20 minutes
from the respective chlorine contact tanks and sludge wet wells. At the end of
the sampling period, the composites were blended to form representative five-
gallon treated effluent and waste activated sludge composite samples. Grab
samples were collected in the same manner as those at the primary effluent
site. Grab samples were drawn at 1200, 2000, and 0400 hours from the east
chlorine contact tanks and sludge wet well on day one; samples were drawn from
the west chlorine tank and wet well at 1600, 2400 and 0800 on day one. This
grab sampling schedule was alternated on a daily basis throughout the 30-day
period.
Samples at the primary sludge location were composited manually. Com-
posite aliquots of two liters were grabbed three times daily, coincident with
grab samples for VOAs, cyanide, oil and grease, and total phenol. Samples were
collected from the sludge wet well via a pyrex beaker attached to a telescopic
sampling pole and emptied into a 2.5-gallon glass jug, which was continuously
iced. The sludge varied greatly in solids consistency and color, not only from
day to day, but also from one grab sample to the next. Samples were taken to
represent as homogeneous a color and consistency as possible. The samples were
collected according to the sludge pumping schedule, usually at 0930, 1530, and
0100 hours.
23
-------
The digester decant, vacuum filter filtrate and tap water locations were
each sampled once per six day period. Samples were normally taken on the third
day of each episode. If the return lines were not discharging on the third day
of an episode, then the samples were collected on the next available day.
Grab samples were also collected during sampling period 16 (February 25,
1981) at the influent, primary effluent, treated effluent, and tap water
locations and were analyzed for asbestos fibers. These samples were taken in
accordance with EPA-Sampling Protocol for Asbestos Self-Sampling. The analyti-
cal results are presented in Appendix A.
Influent, effluent and WAS flow readings, as well as in-situ measurements
for pH and temperature were taken every four hours, coincident with the grab
'sampling schedule. Table 6 lists the daily temperature and pH readings; Table
7 presents a summary of the flow data. The influent flow meter measures the
volume of wastewater pumped to the POTW itself, excluding any wastewater that
is bypassed and including the recycle lines. This meter was calibrated before
the start of the sampling episode. The effluent flow meter records the combined
secondary effluent, bypass, and half the WAS flow that is discharged to the
Tennessee River. The remaining WAS is discharged downstream of the effluent
flow meter. Plant personnel indicated that the effluent flow meter has experi-
enced some calibration problems in the past. Therefore, effluent flow was
calculated by subtracting the primary sludge and WAS flows from the influent
flow. The bypass flows are the only volumes based upon the effluent meter.
Bypass flow was determined by subtracting the influent and half the WAS flow
readings from the effluent readings. Primary sludge volumes were determined by
the number of pump strokes recorded daily. Decant flows were calculated by
computing the change in elevation in the anaerobic digesters; filtrate flows
were estimated by determining the average filtrate volume per hour of operation,
multiplied by the number of hours of operation.
Table 8 contains the sample schedule and the pertinent sampling techniques
for the 30-day study.
QUALITY ASSURANCE/QUALITY CONTROL SAMPLING PROGRAM
During both the six-day study and the 30-day study, quality assurance/
quality control (QA/QC) samples were collected and analyzed. Blank sample
analyses, duplicate wastewater and sludge analyses, and spiked wastewater and
sludge analyses were performed. The blank samples served to identify field
and/or laboratory cross contamination while the duplicate and spike analyses
facilitate precision and accuracy measurements of the analytical results.
Section 5 presents a discussion on the QA/QC program and details the results
observed; additional information is provided in Appendix B. The field proce-
dures for this program are detailed below.
Ultrapure deionized water was pumped through each of the automatic samplers
so that all wetted surfaces in the samplers (silicon and teflon tubing) came in
contact with the "sampler blank." Four liters were collected and forwarded to
the appropriate laboratory for extractable priority toxic pollutant back-
ground information. The sampler tubing was changed every 72 hours to minimize
any possible cross contamination. Composite jugs were changed at the end of
24
-------
TABLE 6. IN-S1TU MEASUREMENTS
ro
Ui
AIR TEMP (°C)
DATE
PERIOD
PRECIPITATION
(INCHES)
MINIMUM
MAXIMUM
INFLUENT
pH
AVE.TEHP
«c
PRIMARY EFF.
PH
AVE.TEHP
°C
TREATED EFF.
pH
AVE.TEMP
"C
PRIMARY
pll
SLUDGE
AVE.TEHP
°C
WASTE ACTIVATED SL.
PH
AVE.TEMP
°C
SEPT. 15
16
17
16
19
20
FEB. 10
11
12
13
14
IS
16
17
18
19
20
21
22
23
24
25
26
27
28
HAR. 1
2
3
4
5
6
7
8
9
10
11
30-DAY
, 1980 1
2
3
4
5
6
,1981 1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
,1981 20
21
22
23
24
25
26
27
28
29
30
AVERAGE
_
-
trace
-
trace
trace
1.94
0.17
-
.
.
trace
trace
0.93
0.44
tf.07
.
-
0.11
.
.
-
.
-
trace
0.05
-
.
0.96
0.10
-
.
_
.
.
-
28
27
18
19
23
22
3
-9
-13
-9
-3
-3
8
10
12
12
6
1
6
5
-1
-2
3
4
-2
8
4
0
5
6
3
2
1
-2
-2
2
32
36
27
32
32
29
12
13
31
7
13
17
18
14
14
19
19
21
18
14
16
21
24
23
22
16
14
12
9
14
12
9
12
14
16
16
9.5
8.4
9.1
8.9
7.6
7.2
8.3
8.8
9.0
8.7
8.5
7.4
8.7
8.0
7.8
8.3
8.5
7.3
7.8
8.8
8.6
9.0
8.8
8.5
8.7
8.3
8.5
8.8
8.2
9.1
8.6
7.8
7.8
8.6
9.3
8.8
13.5
13
14
15.5
16
15
17
16
15.5
IS
15
15
14.5
17
19
18.5
19.5
19
17
i
16
18.5
21
17.5
17
18
17
16.5
19
19.5
19.5
16.8
8.8
8.3
9.0
8.9
7.8
7.0
8.3
8.7
.9
.5
.2
.6
.7
.1
.2
.2
8.5
7.4
7.9
8.9
8.5
8.9
8.7
8.4
8.4
8.6
8.6
8.7
8.2
9.0
8.4
7.7
7.6
8.5
9.1
8.6
13.5
13
13.5
16
16
15.5
17
16.5
16
15.5
16
15
14.5
17
18.5
19
20
18.5
18
16.5
20
20.5
17.5
17
18.5
16.5
16.5
19
21
21
17.1
7.4
6.8
-
8.0
8.2
7.3
7.5
7.5
7.5
7.3
7.0
6.8
6.9
7.2
7.2
7.2
7.5
7.2
7.3
7.6
7.5
7.5
7.6
7.5
7.3
7.4
7.7
7.8
7.8
7.9
7.7
7.6
7.3
7.4
7.8
7.8
14.5
12
12
14.5
16.5
15
16.5
16.5
16.5
16
16
16
14.5
16.5
18.5
19
19.5
19
18
17
19
20.5
19
16.5
18
17.5
16.5
18
20
19.5
17.0
6.2
5.9
7.0
7.2
5.9
6.3
7.1
8.2
8.1
8.5
7.9
7.4
7.0
7.7
7.4
7.6
8.2
7.3
7.5
8.3
7.9
8.0
7.5
7.5
7.6
7.5
7.2
7.7
7.6
7.4
7.7
7.1
7.2
7.5
7.5
7.8
13.5
12
11.5
13.5
16
15
16.5
16.5
15
15
14.5
15.5
15
15.5
17
18.5
19.5
18.5
18
17.5
19
21
19
17
17.5
17.5
17
18.5
17.5
20
16.6
6.9
6.3
7.5
7.4
7.3
6.9
7.2
7.4
7.3
7.3
7.1
6.7
6.6
7.1
7.0
7.3
7.2
7.1
7.2
7.5
7.5
7.6
7.8
7.6
7.5
7.4
7.5
7.5
7.6
7.7
7.4
7.5
7.1
7.4
7.6
7.6
--
—
—
--
—
14
12
13
14.5
16
15.5
16.5
17
16.5
15.5
16
15.5
15
16.5
18
19
19
19
18
17.5
19
20
19
16.5
18
17.5
16.5
18
20
19.5
16.9
-------
TAIll.li /. DAILY H.OWS KOK Tilt SIX-DAY AND TIIIKTY-IIAY STIIDIKS
Dale Period
Se,,l.l5 1
16 2
17 \
IB 4
19 5
20 6
Six Day Average
Feb. 10 1
II 2
12 3
13 4
14 5
15 6
16 7
17 8
18 9
19 10
20 11
21 12
22 13
23 14
24 15
25 16
26 17
21 11!
28 19
Ma: ih 1 20
2 21
3 22
4 2')
:> 24
6 25
/ 26
8 27
9 28
10 29
1 1 30
.JO-Day Average
36-Day Average
Total
lilt 1 lien I
(MOD)
45
36
47
48
42
37
42.5
102.38
9 1 . 59
69.97
40 . 85
43.22
34.40
44.90
76.33
93.98
93.18
44.38
48.97
40.75
43.26
42 . 20
41.82
39.04
36.41
30.95
28.95
37.34
38.02
55.20
50.59
41.20
36.71
30 . 69
40.42
37.20
38.68
49.79
48.58
lilt Incut
to WTI' lly^sa
(MOD) (MOD)
45
36
47
48
42
37
42.5
44.24 58.14
48.58 43.01
50.35 19.62
40.85
43.22
34.40
44.90
39.47 38.86
52.85 41.13
58.23 34.95
44.38
48.97
40.75
43.26
42.20
41.82
39 . 04
36.41
30.95
28.95
37.34
38.02
55.20
50.59
41.20
36.71
30 . 69
40.42
37.20
38.68
42.00
42.1
Primary
Inl lueiil
(MUD)
44.87
35.87
46.87
47.87
41.87
36.87
42. 3 7*
44.35
48.61
50.42
40.90
43.34
34.56
45.03
39.64
52.91
58.29
44.41
49.07
40.86
43.34
42.36
41.98
39. 16
36.56
31. 11
29.08
37.47
38.15
55 . 32
50.65
42.89
36.82
30.85
40.51
37.29
38.80
42.13
42.21
Vacuum
ti It rale
(GI'D)
22,140
22,140
22,140
22,140
22,140
22J40
2 2,1 40*
29,400
28,800
28,700
32,300
-
-
30,900
35,600
30,300
33,000
33,000
-
-
32,600
31,200
32,900
32,600
14,200
-
-
30,600
33,000
26,400
33,400
30,700
-
-
24,300
27,300
33,000
22,140
22,140
Digester
Decani
(CPU)
105,000
105,000
105,000
105,000
105,000
105,000
105,000*
85,100
-
45,700
20,800
118,000
160,000
102,000
131,000
31,100
29,000
-
95,500
106,000
47,700
129,000
89,200
83,000
135,000
164,000
133,000
100,000
100,000
91,300
22,800
664,000
112,000
156,000
66,400
62,300
83,000
105,430
105,430
Primary
Sludge
(Cil'Dj
188,100
188,100
188,100
188,100
188,100
188,100
188,100
125,400
83,600
125,400
188,100
188,100
167,200
185,200
188,100
54,400
73,150
96,400
112,500
114,500
104,500
188,100
188,100
188,100
188,100
188,100
188,100
188,100
167,200
125,400
188,100
188,100
188,100
188,100
131,700
188,100
188^100
162,100
166,400
Primary
Ell luenl
(MCD)
44.68
35.68
46.68
47.68
41.68
36.68
42.18
44.22
48.52
50.29
40.71
43.15
34.39
44.84
39.45
52.86
58.22
44.40
48.96
40.74
43.24
42.17
41.79
38.97
36.37
30.92
28.89
37.28
37.98
55.19
50.46
42.70
36.63
30.66
40.38
37.10
38.61
41.97
42.05
Secondary
Int lueiil
(MOD)
-
-
-
.
-
51.08-
52.86
57.16
58.93
49.35
51.79
43.03
53.48
48.09
61.50
66.86
53.04
57.60
49.38
51.88
50.81
50.43
47.61
45.01
39.56
37.53
45.92
46.62
63.83
59.10
51.34
45.27
39 . 30
49.02
45.74
47.25
50.31
50.45
Helm u
Ac 1 iviildl
Sludge
(MUD)
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.6
Waste
All tVaU-.|
Sluilge
(MOD)
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.29
4.35
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
4.32
Secondary
Ell lueiil
38.12"
39.90
44.20
45.97
36.39
38.83
30.07
40.55
35.10
48.54
53.90
40.08
44.64
36.42
38.92
37.85
39.47
34.65
32.05
26.60
24.57
32.96
33.66
50.87
46.14
38.38
32.31
26.34
36.06
32.78
34.29
37.65
37.73
-------
TABLE 8. SAMPLE SCHEDULE AND SAMPLING TECHNIQUES
Sample Location
Influent
I'riuiary Eft Inent,
Treated Effluent,
Waste Activated
Sludge
Primary Sludge
r'rartion
Acid I
Base/neutral J
Pesticides J
VOA
Netals
COD/TOC/NII
BOU/Residue
Total Plienul
Cyanide
Oil and Grease
Asbestos
Acid 1
Base/Neutral 1
Pesticides J
VOA
Metals
COD/TOC/NII -N
BOD/Residu«
Total Phenol
Cyanide
Oi 1 and Grease
Asbestos
Acid I
Ruse/neutral )
Pesticides J
VOA
Metals
COO/TOC/NH -N
BOD/ Residue
Total Phenol
Cyan i de
Oi 1 and Grease
Asbestos
Preservation
chill
chill
UNO
II Sf3
cfiill
H.PO./CuSO.
NaOir *
(ISO
HgOL^
chill
chillc
UNO
II S6
cfiilT
ILP04/CuSO.
NloHe *
H SO
HgCI*
chill
chill
UNO
II Sd
cfiilT
II PO./CuSO.
NaOir
H SO,
N§ *
Vo 1 umc
it liters
40 ml
1 liter
500 ml
500 ml
500 ml
1 liter
500 ml
1 liter
it liters0
40 ml
1 liter
500 ml
500 ml
500 ml
1 liter
500 ml
1 liter
2 liters
40 ml
1 liter
500 ml
500 ml
500 ml
1 liter
500 ml
NS
Sample Container
glass
glass
plastic
plastic
plastic
amber glass
amber plastic
glass
plastic
glass
glass
plastic
plastic
plastic
amber glass
amber plastic
glass
plastic
glass
glass
plastic
plastic
plastic
amber glass
amber plastic
glass
NS
Sampling Technique
manual composite
grab- lab composited
manual composite
manual composite
manual composite
grab-lab composited
grab-lab composited
grab- lab composited
grab
automatic composite
grab- lab composited
automatic composite
automatic composite
automatic composite
grab-lab composited
grab-lab composited
grab- lab composited
grab
ma n u a 1 compos i te
grab-lab ciiinposi ted
manual composite
manual composite
manual composite
grab- lab composited
grub- lab composited
grab- lab composited
NS
No. of Aliquots
Per Composite
24a
6
24a
24a
24a
6
6
6
1
72
6
72
72
72
6
6
6
1
3
3
3
3
3
3
3
3
NS
Total No.
of Samples
35
35
35
35
35
35
35
35
1
36
36d
36
36
36
36
36
36
1
36
36
36
35
36
36
36
36
NS
-------
TAIIl.K B (
-------
each 24-hour period, scrubbed thoroughly, and rinsed with methylene chloride
prior to reuse. VOA blanks were prepared in the laboratory and then transported
to the field. The hermetically sealed blanks were carried to and from the
sample locations by the field crews, then forwarded to the appropriate labs for
analysis.
Precision and accuracy samples were collected on the first day of each
six-day episode. The volumes for the extractable organics and VOA fractions at
the treated effluent, primary sludge, and WAS locations were tripled during
these periods so that the laboratory could run duplicate analyses and spike
analyses.
OPERATING FACTORS AFFECTING SAMPLING
During the 30-day sampling episode, several occurrences affected the
character of the wastewater samples collected. On February 10, 1981, the day
sampling began, 1.94 inches of rain fell in the Chattanooga area. Because of
the combined sewer arrangement in portions of the Chattanooga service area,
flow to the POTW reached over 100 million gallons (only 44 million gallons
entered the plant; the remaining 56 million gallons were bypassed). Because of
this high flow, pollutants in the influent waste stream were considerably
diluted, directly affecting the solids content of the primary sludge. On this
day and on February 16 and 17 when rain was again experienced, the primary
sludge was wasted only twice each day instead of the standard three times.
Therefore, twice the normal sample volume was collected with the second set of
grab samples on these days and composited with the other sample.
During the rain event on March-4, 1981 (0.94 inches), the bypass pumps
that normally discharge the excess combined sewer flow to the Tennessee River
were not functioning. This situation caused the influent line to the POTW to
surcharge, and a scum layer formed in the influent manhole preventing the
collection of representative samples. Influent data from this sampling period,
therefore, are not included in the summary averages.
Throughout the sampling program, solvent odors were noticed at the in-
fluent location and on February 27, 1981, the odor was particularly more
pronounced. Further investigations revealed that a slug load had been dis-
charged to the POTW. The bar screens at the influent to the plant were clogged
with a gray, gel-like, viscous substance. Plant personnel responded immediate-
ly to the situation by unclogging the bar screens and monitoring the discharge
to minimize the effects of the slug load. A qualitative analysis of the viscous
substance performed by the E.G. Jordan Co. Environmental Laboratory revealed
the following major compounds: chloroform, cyclohexane, toluene, 4-ethenylcy-
clohexane, ethenylbenzene, n-propylbenzene, hexadecanoic acid, linoleic acid,
2-methoxyphenol, 2-methylpropanoic acid, 2-tricecanone, dichlorostearic acid,
tetradecanoic acid and oleic acid. Although this discharge was observed, no
appreciable changes in the influent waste stream character were reflected in
the analytical results for this day in comparison to the other 35 days of
sampling.
29
-------
As noted previously, the aerated grit chamber and wet-air oxidation units
have not been operating for several years. The only mechanical breakdown that
occured during the sampling program involved the shutdown of one of the primary
settling tanks in order to repair several broken slats on the primary sludge
scraper. This lasted frcJm 2000 hours on February 12 to 1600 hours on February
16. The increase in the primary effluent solids concentration reflects this
breakdown. All other treatment components were fully operational during both
the 6-day and 30-day episodes.
30
-------
SECTION 5
DISCUSSION OF ANALYTICAL RESULTS
Daily analytical results for the influent, primary effluent, treated
effluent, primary sludge, WAS, digester decant, vacuum filter filtrate and tap
water locations during the combined 36-day sampling effort are presented in
Appendix C. Summary analyses throughout this report are drawn from this data
base. Daily mass balance analyses are presented in Appendix D.
BACKGROUND POLLUTANT LEVELS
The Tennessee American Water Company supplies water to the city of Chat-
tanooga and surrounding communities. Water is drawn from the Tennesse River
several miles upstream of the MBWWTP outfall and is treated (including chlori-
nating) before distribution. Tap water samples were taken from a faucet at the
MBWWTP once per six-day episode for a total of six times over the 36-day
period. Table 9 presents a summary of the priority toxic pollutants detected
in the tap water.
Dichlorobromomethane was detected 50 percent of the time in tap water
samples at an average concentration of 3 yg/£, but was not detected in any of
the other seven waste streams throughout the 36-day period. The high vola-
tility of this compound may explain this phenonomen. Chloroform was detected
100 percent of the time in the tap water, the influent to the treatment plant
and the secondary effluent from the treatment plant. The average tap water
chloroform concentration (32 ug/fc) represents A3 percent of the average influ-
ent chloroform concentration for the 36 sampling periods.
Toluene and methylene chloride were also detected consistently in tap
water, although at much lower concentrations than chloroform. Methylene
chloride results may be the result of sporadic contamination from field and
laboratory procedures. Bis(2-ethylhexyl)phthalate was observed in 67 percent
of the tap water samples at a mean concentration of 56 ug/£. However, values
ranged from not detected (on two occassions) to 236 Vg/Jt. Because of the wide
variation and limited number of analyses, the average value should be viewed
cautiously. Mercury was detected in the tap water during the initial six day
episode at 9 ug/d, but was not detected in the five subsequent analyses which
suggests that the 9 ug/£ may be a false-positive value.
PERCENT OCCURRENCE ANALYSIS
For each of the priority toxic pollutants, percent occurrence in the
influent, primary effluent, secondary effluent, primary sludge, secondary
sludge, vacuum filter filtrate, digester decant, and tap water samples was
determined. Tables 10, 11, and 12 list the summary percent occurrences for the
36-day, the 30-day, and the six-day periods, respectively. For this evalu-
ation, if pollutants were not identified at or above the pollutant detection
limits, the pollutant was assumed not to be present. For example, the analyti-
cal detection limit for selenium is 1 ug/fc. Therefore, if selenium was not
present at 1 vg/fc or greater, it was assumed not to be present.
31
-------
TABLE 9. SUMMARY OF TAP WATER ANALYTICAL DATA
Tap Water*
Combined 36-Day
Percent
Parameter Occurrence
Chloroform
Toluene
Zinc
Methylene Chloride
Benzene
Bis(2 ethylhexyDphthalate
Dichlorobromomethane
Chromium
Copper
1,1, 1-Trichloroethane
Di-n-butyl phthalate
Cyanide
Ethylbenzene
Chlorobenzene
Trichlorof luorme thane
Chlorodibromome thane
Di-n-octyl phthalate
Antimony
Arsenic
Cadmium
Lead
Mercury**
Nickel
Selenium
Silver
100
100
100
83
67
67
50
50
50
33
33
33
17
17
17
17
17
17
17
17
17
17
17
17
17
Six-Day
Concentration
P8/1
37
1
16
<1
<1
1
11
7
20
ND
<1
50
<1
ND
NO
2
ND
2
2
9
82
9,000
13
2
2
30-Day
Average
MR/1
31
5
33
9
2
67
1
4
11
1
1
1
4
<1
<1
ND
3
ND
ND
ND
ND
ND
ND
ND
ND
Cotnbined-36
Day Average
MR/1
32
5
30
7
1
56
3
5
13
<1
<1
9
4
<1
<1
<1
3
<1
<1
2
14
1,500
2
<2
<1
Secondary
Effluent
36-Day
Average
MK/1
36
54
99
72
4
10
ND
49
19
5
2
92
4
<1
<1
<1
3
1
2
3
15
17
46
1
1
Influent
36-Day
Average
MK/L
74
329
358
82
17
13
ND
226
85
24
5
883
23
1
1
<1
<1
4
4
5
45
309
78
1
8
* Tap water results are based on one sample collected during each six day episode or a total of six
samples during the combined 36-day period.
**
-------
TABLE 10
FERCENt OtCORRtrtCt Or P01LUIAM1 PARAMETERS
CHATTANOOGA 4-KAY AND 30 DAI BWOllB COHtlHflt
F-AkANEfEN
HtNZtHE
METHYIEHE CIILORIPE
f E IRACMLOROE IHYI tMt
CHROMIUM
corptR
BIIVER
2 IMC
CHLOROFORM
T 01. DENE
IMCHI OROEtHYLENt
PHENOL
CTAHIPE
EfHYLfENZENE
I . I . I - tRtCHtOROCrMANC
1 • 2, 4-TRtCMI.OROBEMZENE
MS(2-ElMYl)ltXrL) IHTIIALAU
NICKEL
3,* •(IICHLOROFHEMOL
NAPHtllALCNE
lil-rilCHLOROiitHZEHE
(•I H-tUm FIITHAtATt
l.4-IilCHI.ORO*CNZENE
DlEtllYL PMTMALME
MERCURY
1.2-TRANS-IilCIII OROtTHYLENE
PHENAHTHRtNE
CADMIUM
I.EAO
AR9EHIC
PEMTACIHOROPMEHOl
AMJinOHY
FIUOREME
ACEI4AHITHCNE
CHLOROHCHZf Mt
i H I riiL mot i uoftOHt i MAKE
2>4.«-IRICHLOKnrHEt(0(.
ILUORANIIICNE
SELENIUM
2. 4-l'IHEIlm PHENOL
I . 2-CKIH OkOUHZIHt
KRYLL1IIM
IllAltlun
1.2-UIMItMTl Hrl'kA/IMl
BISCVCMtOROErtfirOXir) MtlllAWE
MOTYt. BENIYL FHIIIAIAU
if i i>icmn*i>EmAMr
I , I- HCHI OtUIEUm ENl
ArENAFHUIYt.ENt
CAKACItl ORUtltlA CRtSOI.
•J CHI tlMJflllNOL
F-lttlUtAMTB MO I I ISIEt' MtkE NtVER tlCICCUP
ptsiicit'ts utnt. ASSUMED HOT
HllfU'ERG IN PARCNIHtSEB ARC (HE IQIAI WIMPIK OF SAHfLES IAKLH
1NFC
100 (391
100 US)
100 (33)
100 (33)
100 (33)
100 (35)
100 (33)
V? (33)
97 (33)
97 (33)
97 (33)
t7 (33)
89 (33)
at 133)
83 (33)
B3 (33)
77 (33)
74 (33)
71 (13)
49 <33)
to mt
37 (35)
37 (33)
37 (33)
4V 1331
44 (33)
41 (33)
44 (331
37 (33)
34 (33)
31 (33)
It (33)
29 (33)
23 (35)
10 (31)
20 (33)
20 (33)
20 (33)
20 (J3>
20 133)
17 (33)
17 (33)
17 (331
17 ( 13 )
14 (33)
14 <3S)
14 (33)
11 (33)
II (35)
11 (33)
» (33)
V (35)
PRIM
EFfL
100 (34)
97 (3t)
100 (34)
100 <34)
100
100 (34)
100 <34)
100 <3A)
97 (3A)
97' (34)
94 <34)
97 <34)
94 <34)
B4 (34)
Bl <3A!
73 (34»
78 43«)
73 (34)
3* (341
41 43«>
94 (34)
47 (34)
41 (34)
39 (34)
72 134)
47 (34)
34 (34)
90 (34)
31 (34)
3J (34)
23 (34)
23 (34)
22 (34)
11 (34)
20 (34)
17 (34)
17 <34)
28 (34)
l» 134)
17 (34)
19 (34)
19 (34)
14 (34)
It (34)
8 (34)
II (34)
14 (34)
* (34)
4 (34)
II (34)
4 1341
3 (34)
SEC
EFFl
100 (33)
100 (33)
•4 (331
92 (341
49 134)
04 (34)
100 13*1
100 (33)
97 (33)
37 (351
94 134)
100 (341
40 133)
94 (33)
49 134)
94 134)
30 (34)
44 (34)
23 (341
4] (341
42 (34>
17 (34)
SO (34)
4 (341
0 (351
3 (34>
20 (34)
22 U4t
22 (34)
0 (34)
17 (34)
22 (34)
II (34)
19 (34)
4 (331
14 (35)
32 (34)
3 (34)
0 (34)
17 (34)
34 (34)
8 (34)
0 (14)
I/ (341
0 (34)
(J4)
(34)
(33)
(33)
(34)
(34)
4 (34)
PRIM
BLUUOE
98
44
47
100
100
100
100
09
97
97
94
100
97
33
92
42
100
0
94
0
11
90
3
64
19
89
94
100
100
90
3
89
33
19
29
3
0
89
49
14
0
31
89
0
0
0
23
28
0
e
0
0
(341
(34)
(341
(341
134)
(341
(34)
(34)
(14)
(341
(14)
(34)
(341
(34)
(14)
(341
(34)
(141
(14)
(14)
114)
(14)
(141
(14)
(34)
(34)
(34)
(141
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
134)
(34)
(34)
(34)
134)
(34)
(14)
SEC
BlUPOE
29
14
30
100
100
100
100
81
47
14
1
100
42
a
78
19
100
0
39
0
3
0
0
22
0
4
84
97
100
4
3
93
0
0
4
0
0
17
8
14
0
1
89
0
0
0
1
0
0
3
0
0
1141
(34)
(14)
(34)
(14)
(141
114)
(34)
134)
(34)
(34)
(341
(34)
(341
(34)
(34)
(14)
(14)
(34)
(34)
(14)
(14)
(It)
(14)
(14)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(34)
(14)
(14)
(14)
(14)
(34)
VAC PUT
FUIRATE
83
83
0
100
100
100
100
0
100
0
81
30
33
17
17
100
47
31
34
31
31
17
100
90
0
50
17
47
30
30
17
17
31
0
0
17
17
17
17
17
17
17
0
17
33
33
0
0
0
17
0
17
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
41
4)
41
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4>
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
DIGESTER
BUFERMATNT
100
100
0
100
100
100
100
17
100
0
81
80
100
33
30
100
too
17
47
83
03
83
47
100
100
83
100
)DO
47
47
0
33
33
17
100
17
0
30
33
17
0
17
30
17
17
17
17
30
0
0
17
0
41
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
3)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
41
4)
4)
4)
4)
4)
4)
4)
4)
4)
41
41
4)
4)
4)
4)
4)
4>
4)
4)
( 4)
( 4>
IAI-
UAtCR
43- 4)
821 4)
0 4>
3d 4)
9(> 4)
17 4)
100 4 )
10* 41
I0(> 4)
(> 4>
<• 4)
3: 4)
1)' 4)
33 4)
(i 4)
4'/ 4)
i; 4)
(< 4)
(> 4)
<• 4)
3>. 4)
(< 4)
(' 4)
i; 4>
(< 4)
(> 4)
j; 4>
n 4>
1) 4)
C 4)
(> 4)
1) 4)
C 4)
e 4)
i; 4)
1' 4)
( 4)
e 4)
C 4)
17 4)
C 4)
C 4)
C 4)
C 4)
C 4)
(< 4)
C 4)
C 4)
0 41
(> 4)
0 4)
O 4)
-------
u>
1,1,? TRICHLIIRIIIIIIAME
I,|i2>3- lEIRACMLOKOIIMANE
1,2 lilClltOKOf KOPANE
i. JD inn OKnii.-or vi EWE
cm URDU I URummi: THANE
.',4 UlHIIHOflllHOI.
UAHMA KIC
CAKHOM TEIKACMIOKII'E
|,2-(iICm.ORUEniANC
hCIIKL CHIORM'E
VINTI. CIILOKtl'E
4-NI1kOF>irMOL
HaCJ-CMLOKOEIMILI CIHEft
N MIfhOBQIU-N-F-ROPYlAMINE
(U -N OCTYl PHTHAlAlt
PIHEIHU IHIIIAIATE
1,3-KMZANHIRAClHE
ALfHA-miC
l.-Ml(>ROC THANE
JHCIIIOROUIFI UOROMetHANt
2-NIIRUHlEHni
KEHtll'lNt
HtXACIII OUIPHENUAntN£
»CN20 (A)PYRENi:
I I i 12-liENWlUORANIHI.NE
1 i 12-BEN/OF-tfiYI ENE
1.215,4 I'lbCNIAMIMfcACEHE
IM|itH((( I , Jr J-L.IH
INl/MH ALI>Ut
lit I FA ftllC
TABLE 10
f-CKCENt OCCURRENCE OF FOUU1AMI PARAMETERS
CIIATTANDOUA 1-l'AY ANH 30-IMV tfUIOIEB COntlHCH
f'RI
INft IFF
« (33>
i
3 <33>
0 (33>
0 (33)
0 (33)
0 (33)
0 (35)
0 (33)
0 (33)
0 139)
0 (33)
0 (39)
0 (13)
0 (39)
0 (33)
0 (33)
0 <3S>
0 (39)
0 135)
0 (39)
o ct;;>
0 (33)
0 (33)
H 61 C fKlh (EC
L CFFl flLUHUE BlU
<3«> 3 (33) 42 (3*>
131) 3 133) 3 (31)
(31) 0 (33) 0 (31)
(31) 0 113) 0 (31)
131) 0 (33) 0 (31)
131) 0 (311 0 131)
(3&> 0 (31) ii 131)
<31) 0 (31) 0 (31)
(31) 3 (31) 0 (31)
(31) 0 (33) 0 (31)
(31) 0 (33) 3 (31)
(31) 0 (33) 0 (31)
(31) 0 (33) 3 (31)
131) 1 (31) 0 (31)
(31) 0 (31) 0 (31)
(31) 0 (31) 0 (31)
(31) B (34) 3 (31)
(31) M (31) 0 (31)
(31) 0 (31) 31 (31)
(31) 0 (31) 1 (31)
(31) 0 (33) 0 (31)
131) . 0 (33) 3 (31)
131) 0 (33) 3 (31)
(31) 3 (31) 0 (31)
(31) 0 (31) 0 (31)
(31) 0 (31) 0 (31)
(31) 0 (31) ) (31)
(31) 0 (31) 0 (31)
(31) ft (31) 3 (31)
(31) 0 (31) 3 (31)
(31) (31) 0 (31)
(31) (31) 0 (31)
(311 (31) 0 (31)
(31) (31) 0 (31)
(11) (31) B (31)
(31) (3«) 1* (31)
(31) (31) 0 (31)
(31) (31) 0 (11)
(31) (31) 3 (31)
0 (31) (31) 0 (31)
0 (31) (31) 0 (31)
VAC Fill
HUE fILTHAIC
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) .0
(3D 17
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) «
(31) 0
(31) 0
(11) 33
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(31) 0
(11) 0
(31) 0
(31) 0
(31) 0
0 (31) 0
(ilOEBTER
SUPEKNAIHI
1) 0
1) 0
A) 0
1) 0
1) 0
1) 0
1) 1?
1) 0
1) 0
4) 0
1) 0
4) 0
1) 17
4) 0
1) 0
1) 0
1) 4?
4) 0
1) 17
4) 0
1) 17
1) 0
1) 0
1) 0
1) 0
1) 0
1) 0
1) 0
1) 0
4) 0
4) 0
4) 0
4) 17
4) 17
4) 0
4) 0
4) 17
4) 13
1) 0
4) 17
1) 17
IAP
UAIiR
1) 0
1) 0
4) 0
4) 0
1) 17
4)
1)
4)
1)
4)
1)
4)
4)
1)
4)
4)
1) 1 '
1) '
1) i
1) 1)
1) II
1) 3d
1) 0
1) <>
1) 0
4) •>
A) 0
1) 0
1) 0
4) 0
4) 0
4) 0
4) 0
4) 0
1) 0
4) 0
1) 0
1) 0
1) 0
1) 0
1) 0
1)
1)
1)
1)
1)
11
1)
1)
1)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
4)
1)
1)
1)
1)
1)
1)
1)
1)
1)
4)
1)
1)
11
1)
1)
1)
1)
1)
4)
4)
4)
»OLllir*M|[i HOI I limi> UtKE NEVER UETCC1Ei<
IINCONF IKnEli FESIICK'ES Utfct ASSIIMtt' NUT 1'EIECIED
IN fAhtnuniiis AM HIE roiAi NUM&EK OF SAMPLES TAKEN
-------
TABLE 11
PtkCEHI OCCURRENCE OF POLLUTANT MRAMtlEfcS
CHATTANOOOA 30-I>AY SlUtiY
Ln
BENJENE
HETHYIENE CHLORITE
TEIRACHI.OROETMYI.EME
CHROMIUM
COPPER
SILVER
ZINC
CHI.OROFOKH
TOLUENE
TRICIILOKOETIIYLENE
PHENOL
CYANI HE
ETHYL BENZENE
1>1iI-1RICHLOROETHANE
I.2.4-IR1CHLOROBENZENE
li3-DtCIU.OMJtiEN7.ENE
11942-EmLIIEXTL) PHTHALATE
2.4-DICHIOROPMENOL
NICKEL
NAPHTHALENE
MERCURY
DI-N-BUIYL HITHALA1E
(•4-DICHLOROBENZENE
DIEIHVL PHTItALATE
li2-TRAMB-DICHLOROETHYLENE
ANTHRACENE
FLUOftENE
PHEMANTIUiENE
CAI'HIUH
LEAD
ACENAPIUHENE
1*I CHIOKOFLUOROME THANE
ARSENIC
2.4-DIHETIIYLPHENOL
TLIIIIRANTMENE
PYKINI
PttHACIII OftOPHENOL
1,3 I'lHIENII Hrl'ftAZIMr
eis<2M in cmoEiimixY) METHANE
ANIIHOHY
CHI OK06tN/tNt
I > I -PICIILOMIt IIITI tNE
2> 4i«-TRICMlOROPHENOL
ACEMAPIITHYLENE
BERYLLIUM
I>I-DICIIL«RUEIIIANE
PARACIIIOROMEIA CKESOL
2-CHLORnPH«:MQL
I.I>2-TRICHLOROElHANE
I i I r2>2-IETRACIILOROCTHANE
Ii2-DICHLOROPROPANE
I . J-HICHLOROPkOPYLENE
CHLUKOnitlRimCmEIHANL
Pill I UIANTS Mill LISIEtl UfkE NEVER I'fUCILI"
IIMIONMKMtli PESTICIDES UERE ASflllMEP NOT UEIECIED
MUMPERS |N PARtNlllt S( B ARE HIE TOTAI NUMBER Or SAMPLES
I NFL
100 (2*1
100 (2»t
100 (29)
100 (2*1
100 (29)
IDA (29)
100 (29)
97 (29)
97 (2V)
97 129)
97 (29)
97 <29I
84 (29)
83 (291
79 (291
79 (29)
79 (29)
72 (29)
72 1291
At (29)
4* (29)
32 (29)
48 (29)
48 (29>
41 (29>
30 (29)
34 (29>
34 (29)
34 (29>
34 (291
28 (29>
24 (29)
24 (29)
21 (29)
21 (29)
21 (29)
17 (29)
17 (29)
17 (29)
17 (29)
14 (29)
14 (291
14 (29)
14 (29)
14 1291
10 (29)
10 (29)
10 (29)
7 (29)
7 (291
7 (291
7 (29)
7 (29)
PRIH
EFFL
100 (30)
97 (30)
100 130)
100 (30)
100 (30)
100 (30)
100 (30)
100 (30)
97 (30)
97 (30)
93 (30)
97 (30)
93 (30)
83 (301
77 (30)
73 (301
70 (30)
73 (301
71 (30)
47 (30)
47 (30)
47 (JO)
«0 (30)
93 (30)
47 (30)
40 (30)
27 (30)
37 (30)
23 (30)
40 (30)
13 (30)
20 (30)
17 (30)
23 (30)
33 (30)
23 (30)
13 (30)
10 (30)
13 (30)
10 (301
27 (30)
7 (30)
13 (30)
13 (30)
13 (30)
10 (30)
7 (30)
3 (30)
10 (30)
0 (30)
0 (30)
0 (30)
0 (30)
SEC
EFFl
100 (30)
100 (30)
83 (30)
90 (30)
47 (30)
83 130)
100 (30)
100 (30)
97 (30)
43 (30)
93 (30)
100 (30)
40 (30)
SO (30)
43 (30)
SO (30)
47 (30)
40 (30)
SO (30)
10 (30)
7 130)
30 (30)
20 (30)
SO (30>
0 (30)
0 (30)
13 (30)
0 (30)
13 (30>
10 (30)
1] (30)
17 (30)
7 (30)
37 (30)
3 (30)
0 (30)
7 (3»>
0 (30)
3 (30)
7 (30)
7 (30)
7 (301
13 (30)
3 130)
0 (30)
0 (30)
3 (30)
7 (30)
3 (30)
3 (30)
0 (10)
0 (301
0 (10)
PRIM
SLUHQE
40
33
47
100
100
too
100
93
97
100
43
100
97
40
93
0
30
0
100
97
97
0
43
3
3
47
43
93
too
too
23
0
100
0
90
47
3
0
0
87
13
0
0
10
100
17
0
0
SO
3
0
0
0
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(301
(30)
(30)
(30)
(30)
(30)
130)
(30>
(30)
(30)
(30)
130)
(30)
130)
(30>
(30)
(30>
(30)
(30)
(30)
130)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(301
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(10)
SEC
SLUDOE
13
10
30
100
100
too
100
77
37
30
0
100
30
10
87
0
7
0
100
43
13
3
0
0
0
3
0
3
100
97
0
0
100
0
20
10
3
0
0
47
3
0
0
3
100
0
0
0
7
0
0
0
0
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
130)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30)
(30>
(30)
(30)
(30)
(30)
(30)
(30>
(30)
(30)
(30)
(30)
430)
VAC fill
FllTMU
100
100
0
100
100
100
100
0
100
0
ao
40
40
20
0
40
100
20
40
40
40
20
20
100
0
40
40
40
0
40
0
20
40
20
20
20
0
40
40
0
0
0
0
20
0
0
0
20
0
0
0
0
0
a>
9)
3)
S>
3)
3)
S>
S)
3)
3)
3)
31
S)
S)
S)
3)
31
3)
3)
S)
3)
SI
S)
S)
3)
SI
3)
S)
3)
3)
S)
S)
3)
3)
3)
3)
5)
31
3)
S)
S)
3)
3)
3)
3)
3)
3)
3)
3)
3)
S)
S)
3)
DIGESTER
SUPERNATMT
100
100
0
100
100
100
too
20
100
0
BO
eo
100
40
40
100
100
0
100
60
100
BO
BO
40
too
00
40
eo
100
too
20
20
40
0
40
20
0
20
20
30
100
0
0
0
40
40
20
0
0
0
0
0
0
IAP
WATER
3) 80
3) 100
3) 0
3) 40
3) 40
3> 0
S) 100
3) 100
3) 100
3) 0
S) 0
3) 20
3) 20
5) 40
3) 0
3) 0
3) 40
3) 0
3) 0
3) 0
3) 0
3) 40
9)
3)
3)
S)
3)
3)
3)
3) 0
3) 0
S) 20
S> 0
3) 0
3) 0
3) 0
31 0
3) 0
3) 0
3> 0
3) JO
3) 0
3) 0
3) 0
3) 0
3) 0
3) 0
3) 0
3) 0
S) 0
3) 0
3) 0
3) 0
S)
3)
3)
S)
3)
S)
3)
S)
3)
3)
3)
S)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
S)
5)
S)
31
3)
3)
31
3)
3)
3)
3)
S)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
TAKEN
-------
U>
TABLE U
OCCURRENCE or FOUUIAHI
CIIAIlANOOOA JO-DAI
I AKAHt-ltH
CHR1T9ENC
CAR»ON TETRACIUQMC'E
I>2-I>ICIII OkOE THANE
AC TIIU L' lit Oft) lit
VINTL CIILORIM
« NllftOMIfHOL
Biei2-CMtOkOCrHYL> ElMEk
M NllfcOtiQI>I-N-PkOPU.AI11NE
UI-N-OCTU HiTiiAiAiE
PlttEIHU rill MAI A IE
BCtrNIUH
ClllOftOETMAME
P I CHI OROkROHOHE 1 MANE
2-NllftOPIIEHOL
btNZIDIHE
lltXACmORObtHIEHE
IIEXACIII OftOElllAHf
7-CIII.ORONAFHTIIALEMC
2»«-PlNlIROiaillCNC
4-CIII OkUHIf NU PHENU ElltE*
• ISC-CHLOKOIttOFROPVL) EIIIER
ISOPHOfcONt
HI1kO«LN(ENE
M HI IdOSQlUf MtNII.ANIME
bUfTl tEMZTL
*ENZO
i>2IS,6-bItlEHZANnilcACEME
na>eNo2ii c.o
AIT HA -MIC
PRIH SEC PRIM SEC VAC MLT DIOCSIIR TAP
inn em trn tiunot aiuuut rurMiE IUPCKNAINI UAIER
7 (IV) 10 (J0» (JOt 0 (10) 0 17 4101 7 4101 20
(If»
(If 1
(IV>
(5t)
I2»>
(2tt
(2V >
(29) I
<2f > 1
(3»>
I2»>
Of)
(If >
0 (2T»
0 (2V>
0 <2»)
(2f 1
(If >
I2t>
(If)
(2f )
(IV) 1
(2f »
<2f )
(2f >
<2fl
(2f >
<2»>
(2f )
(2f >
(2f >
(If)
<10> (10> <]0) 0 410)
(10) (10) 410)
(10) (10) 410)
(10) 110) 410)
(10) (10> 410)
(10) (10) 410)
(10) 0 (10) 410)
(10) 10 4101 4101
(10) 10 110) 0 (101
(10)
410)
410)
(10)
110)
110)
(10)
4101
(101
(JO)
410)
(JO)
(10)
(10)
(10)
(10)
430)
(10)
110)
110)
(10)
(10)
(10)
(10) JO 410)
(10) 1] (10)
(10) 0 410)
110) « 410)
(10) 0 410)
(10) 0 410)
110) 0 410)
(10) 3 410)
410) 0 4JOI
(30) 17 410)
410) 3 410)
(10) 1 410)
(10) 0 410)
(10) 0 (10)
(10) 0 410)
(10) 0 410)
410) 17 4J0)
110) 10 (10)
<10> 21 410)
(10) 0 110)
410) 0 410)
410) I 410)
410) 1 410)
430)
410)
410)
430)
410)
410)
410) 4
410)
410)
110)
410)
410)
(10)
410)
410)
430)
430)
430)
430)
410)
410)
410)
410)
410)
430)
(30)
430)
410)
410)
(10)
410)
S) 0
31 20
9)
3)
3)
S)
3)
3)
3)
31 t
3)
3) 2
3)
3)
3)
3)
3)
3)
3>
3)
3)
3)
3)
3)
3)
3) 2
3) 2
3)
3)
3)
3) 2
3) 4
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
at i
3)
3)
3)
3)
3) 4
31
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
31
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
31
S)
3)
3)
3>
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
3)
31
3)
rOHUIANIS MO! LISIfli HIM NEVER M.IECTEP
risricicrs UCKC ASSUHII- ttoi t>ttc.citti
IN i-AfclNMIESES ARE HIE fUTAL NUMBER OF 8AMPI £8
-------
TABLE 12
flflCENf OCCURRENCE OF FOllUIAMI f'ANAHEIEKB
CHATTANOOGA 4-DAJ BIUIlT
PAftAMEIER
I'EN/EHE
liltl-TKlCHLOftOEIHAHE
CHI OROFORM
EmrLPENZEHE
HEIIIYIENE CIILORIliE
IEHACIII OROETHUEHE
IIHUENC
IMCHlOKUtlim ENE
Ull MOL
1.2.4-TRICHLOROftENZENC
I . 2-HICIItORUdENZEHE
NAPHTHALENE
»l!><2-EIHYLIfEXYLI PHIIIALATC
DI-N-tUTTL flllMALAlE
METHYL PMTHALATE
FHENAN1 (IRENE
AM t I MOM I
ARSENIC
tfll'MIUH
CIIKOI1IUM
CTANIKE
IEAII
NICKEL
EEIEMIUM
SILVER
TMALLIUH
ZINC
1.2-lKANS-DICHLOfcOETHri.ENE
2'1-PlCULDftOfUtNtlL
unii »ENZYL PHIIIALAIE
CMl OROfEHZENE
2t 4t A- TftlCIILOROtllENUL
Al f-MA-FNPOSIILFAN
OAMHA-bllt
SERtlLIUM
I . I -I'ICIII UKOE THANE
li3-|i|CIHOI(OI4-(IIHETHYIPHENOL
AeENAPMIHCNf
POI I U1AM1S NO I LISIIl' UtKE NEVER I'ETECIEP
UIICDHUkHLD 1-fBI 1C ItitS Ullif ASSUHili HOt
NlmlrERS IN (AREHIIIESES AhE IDE TO1AI MllMfcER
INFL
100
100
100
100
100
100
100
100
100
too
100
100
100
too
100
100
100
too
too
100
100
100
100
too
100
100
100
100
100
100
83
81
ei
30
so
3J
31
31
17
17
17
17
17
17
17
0
0
0
0
0
0
0
0
PRIM
EFFl
41 100
41 100
61 100
41 100
41 100
4) 100
4t too
41 100
4t 93
41 100
4) 100 •
41 100
4) 109
41 100
4) 100
4) 100
41 100
41 100
4) 100
4) 100
4) 100
41 100
4) 100
41 100
41 100
4) 100
4) 100
At 100
4) 100
4) 100
4) 100
41 01
4) 47
4) 31
4) 31
41 0
41 17
4) 17
4) 0
4) 0
4) 0
4) 0
4) 0
41 0
4) 0
4) 0
4) 0
4> 0
4) 0
4) 0
41 0
4) 0
4) 0
SEC
KFFL
41 100
4) BO
4) 100
4) 40
4) 100
4) 100
4) 100
4) 20
i> 47
4) 100
4) 100
4) 11
41 0
4) 100
4) 100
4> 100
4> 100
4) 17
4) 100
4) 100
4> 100
41 100
4) 81
4) 100
4) 81
4) 100
4) 100
4) 100
4> 100
4) 100
4> 0
4> 83
4) 11
4) 0
4> 47
41 0
4) 17
4) 0
4) 0
41 0
4) 0
4) 0
4)
4)
4)
4)
4)
4)
4)
4)
4)
( 4> 11
( 4) 30
f-RIH
siunoE
31 SO
31 0
3> 47
3» 100
31 100
S> 47
9) 100
3) 81
t) 0
41 17
4) 81
4) 0
4) 83
4) 81
4) 100
4) 47
4) 0
41 47
4) 100
4) 100
4> 47
4) 100
4) 100
4) 100
4> 100
4) 100
4) 17
4) 100
4) 0
4) 100
9) 100
4) 0
41 47
S» 81
41 0
41 0
4) 0
4) 31
3) 81
4) 30
4) 81
4) 47
4) 81
4) 0
4> 11
3) 0
3) 17
3) 17
3) 17
3) 0
9) 0
41 0
4) 0
SEC
SLUDOE
4) ei
4t 0
4) 100
41 100
4) 11
4) 100
4) 100
4) 47
4) 0
4» 17
4) 11
4) 0
41 0
4) 17
4) 83
4) 0
4) 0
41 17
4) 81
4) 100
41 17
4) 100
41 100
4) 100
4) 100
41 100
4) 81
4) 100
4) 0
4) 100
4) 0
t> 0
4) 0
4) 17
4) 0
41 0
4) 0
4) 31
4) 0
41 0
4) 0
4> 17
4) 0
41 0
4) 47
4) 0
4> 0
4) 0
4> 17
4) 0
4) 0
41 0
4) 0
VAC Fill
FIL1RA1E
4) 0
4) 0
4) 0
4) 0
4) 0
41 0
4) 100
4) 0
4) IOO
4> 100
4> 100
4) 100
41 0
4) 100
4) 100
4) 100
4) 100
6) 0
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 100
4) 0
A) IOO
4) 0
4) 0
4> 100
41 0
4) 0
4) 0
4) 0
41 0
4) 0
4) 0
4) 0
4) 0
4> 0
4) 0
4) 0
4) 0
4) 0
4) 0
4) 0
4) 0
1 4) 0
(ilOEBfER
BUPERNAINT
1 ) IOO
1) 0
1 > 0
1 1 IOO
1) 100
1) 0
1 > 100
1) 0
1) 0
1) IOO
1) IOO
It IOO
1) 100
I) IOO
1) IOO
II 100
1) IOO
i> too
i) loo
1) IOO
1) IOO
II IOO
1 1 100
II 0
1) 100
1) IOO
II IOO
1 1 IOO
1) IOO
1) 100
1 ) IOO
t> 100
II IOO
1) 100
It 0
1 1 0
It 0
1) IOO
1 ) 0
II 0
1 t IOO
1) 0
1) 100
It 0
II IOO
It IOO
It 0
II 0
1 t 0
II 0
1) IOO
II 0
II 0
IAP
UAIIR
II 0
11 0
11 IOO
II 0
11 0
II 0
It IOO
It 0
It 0
11 0
1 t 0
It 0
It 0
It 0
It IOO
It 0
II 0
It 0
it loo
II IOO
It IOO
It IOO
it too
) IOO
It IOO
It 100
It IOO
It 100
II 0
It 100
II 0
It 0
II 0
11 0
II 0
II 0
It 0
II 0
It 0
11 0
II 0
It 0
It (
It ('
II 100
II 0
It 100
II 0
It 0
It 100
It 0
1 t 0
It 0
1 1
II
1 1
1 1
II
II
1 1
II
It
1 1
It
1 1
It
II
1)
It
II
II
II
II
1 1
II
II
1 1
1 1
It
1 1
1 1
II
It
II
1 1
1 1
1 1
1 1
1 1
II
1 1
1 1
II
1 1
1 1
II
II
1 1
1 1
II
It
II
It
1 1
11
It
(IF SAHHES TAKEN
-------
TABLE 12
ClkCENT OCCUkKENCE OF fOLLUTAMI fAfcAlttUfcS
4-MT stuj*r
rAHAHEUM
ni-H-OCIVI PMIIIAIAH
HI tit I lit I FtlTIIALATt
iwrt
PKIH
fffL
IEC
fffL
CHftVSENE
ENIiftlft ALIiCHTIiL
I'fLM-HIC
0
0
0
0
0
0
41
41
41
41
41
41
• 0
0
0
0
0
0
41
4)
4)
4)
41
41
0 1
11 (
0 1
0 <
0 (
0 <
4>
4»
41
41
4)
4>
Ml IN
SIUD£
0
0
11
11
0
0
E
t 41
( 4»
( 4>
1 4>
( 4>
( 4>
EEC
BLUHOE
0
0
0
0
0
0
41
4)
4)
4>
4)
4>
VAI
fll
: rui
FHATE
I)
1)
it
i>
I)
I)
PIDESICR
SUfEHNATNI
too
0
0
0
100
100
l>
1)
1)
l>
1)
It
ii
I)
it
i)
I)
oo
F-OUUIAMTS HOT iistrri ucttt ntvf« i
-------
Analytical results for influent waste stream samples indicate that, during
the combined 36-day sampling study, 72 pollutants were detected at least once,
24 were detected at least 50 percent of the time and seven pollutants (benzene,
methylene chloride, tetrachloroethylene, chromium, copper, silver, and zinc)
were detected during each of the 36 periods. Percent occurrences for the
30-day period are similar, (i.e., 66 pollutants detected at least once; 22
pollutants detected 50 percent or more of the time; and the seven pollutants
listed above detected 100 percent of the time).
During the six-day study, 45 pollutants were detected at least once in the
influent including six pollutants (alpha-BHC, gamma-BHC, alpha-endosulfun,
buthyl benzyl phthalate, thallium, and 1,2-dichlorobenzene) that were not
detected during the 30-day study; 35 pollutants were detected a minimum of 50
percent of the time in the influent; and 30 pollutants were detected 100
percent of the time. A comparison of the six-day and 30-day data indicates a
substantial reduction in the number of pollutants detected in the influent 100
percent of the time during the 30-day study and a corresponding increase in the
number of pollutants identified at least once during that study. This is also
true for the other waste streams sampled and results from the increased time
span during the 30-day study and the diversified industrial character of the
wastewater, respectively.
Table 13 contains the influent waste stream priority toxic pollutant
percent occurrences, average concentrations, minimum concentrations, and
maximum concentrations for the six-day and 30-day studies and for the combined
36-day study. If a pollutant was not detected above the analytical detection
limit of that compound, the concentration was assumed to be zero and zero was
used to calculate the average concentration values. As expected, due to the
extended sample collection period and subsequently greater data population
during the 30-day study, both the total number of pollutants detected and the
range of concentrations for most pollutants in the influent waste stream were
observed to be greater for the 30-day study than for the six-day study.
Results of a comparison of the pollutants occurring in the secondary
effluent during the six, 30- and combined 36-day periods are similar to the
results of the comparison of the pollutants found in the influent during those
studies. A total of 53 toxic compounds were detected during the combined
36-day period, in contrast to only 36 pollutants during the six-day period and
48 pollutants during the 30-day period. However, 21 pollutants occurred 100
percent of the time during the six-day period, compared to only five pollutants
(benzene, chloroform, methylene chloride, cyanide, and zinc) during the 30- and
combined 36-day periods. Table 1A presents a comparison of the percent occur-
rences, mean concentrations and range of the secondary effluent concentrations
for the six-, 30-, and combined 36-day studies.
For the combined 36-day study, eight priority toxic pollutants (seven
metals plus cyanide) were detected in the primary sludge 100 percent of the
time. Phenol was the only acid extractable organic compound observed to occur
repeatedly in the primary sludge during the 36-day period. Base/neutral
pollutants observed to concentrate in the primary sludge during the combined
36-day period were 1,2,4-trichlorobenzene, 1,4-dichlorobenzene, fluoranthene,
naphthalene, bis(2-ethylhexyl)phthalate, anthracene, fluorene, and pyrene.
Results of both the six-day and 30-day studies indicate that certain metals
concentrate in the primary sludge to a significant degree.
39
-------
TABLE 13. COMPARISON OF THE SIX-DAY, 30-DAY, AND COMBINED 36-DAY INFLUENT PRIORITY POLLUTANT CONCENTRATIONS
Six-Day Study
Percent
Parameter Occurrence
Benzene
1 ,'J , l-Trichloroethane
Chloroform
Ethylben/.ene
Methylene Chloride
Tetrachloroethylene
Toluene
Trichloroethylene
Pentachlorophenol
Phenol
1,2,4-Trichlorobenzene
1 ,2-Dichlorobenzene
1 ,4-Dichlorobe«zene
Naphthalene
Bic(2-etuylhexyl) Phthalate
Di-n-Butyl Phthalate
Diethyl Phthalate
Phenanthrene
Antimony
Arsenic
Cadmium
Chromium
Copper
Cyanide
Lead
Nickel
Selenium
Silver
Thallium
Zinc
1 ,2-Trans-Dichloroethylene
2,4-Dichlorophcnol
Butyl Benzyl Phthalate
Chlorobenzene
2,4,6-Trichlorophenol
Alpha-Endosulfan*
Carama-BHC-'
Beryllium
1,1-Dlchloroethane
1 ,3-Dichlorobenzene
Fluoranthene
Anthracene
Pyrene
Alpha-BHC*
Mercury*
100
100
100
100
100
too
100
too
100
100
100
100
100
too
100
100
100
100
100
too
100
100
100
100
too
too
100
100
too
100
83
83
S3
SO
50
33
33
33
17
17
17
17
17
17
17
Average
Concen-
tration
(UB/D
13
43
77
23
40
81
378
10
;*
44.B
100
7
4
55
14
4
6
3
12
9
10
226
123
4,747
136
98
3
21
:i
486
2
2
3
I
3
617
967
<1
1
<1
<1
1
-------
TABLE 13. COMPARISON OF THE SIX-DAY, 30-DAY, AND COMBINER 36-DAY INFLUENT PRIORITY POLLUTANT CONCENTRATIONS
Six-Day Study .
Percent
Parameter Occurrence
Trichlorofluoromethane
Chlorodibromomethane
Vinyl Chloride
2,4-Dimethylphenol
Accnapthlenc
Di-n-octyl Phthalate
Dimethyl Phthalate
1 ,2-Benzanthracene
Chrysene
Fluorene
1 ,2-Diphenylhydrazine
Bis(2-rhloroethyoxy)methane
1 , 1-Dichloroethylene
Acenaphthylene
Parachlorometa Cresol
2-Chlorophenol
1 , 1 ,2-Trichloroethane
1 , 1 ,2,2-TetrachIoroethane
1 ,2-Dichloropropane
1 ,3-Dichloropropylene
2,4-Dinitrophenol
Carbon Tetrachloride
1 ,2-Dichloroethane
Methyl Chloride
4-Nitrophenol
Bis(2-chloroethyl)ether
N-Nitrosodi-N-Propylamtne
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
Average
Concen-
tration
(U8/1)
HD
m
m
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Maximum
Concen-
tration
(MB/I)
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Minimum
Concen-
tration Percent
(V8/1) Occurrence
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
24
7
3
21
28
3
3
3
7
34
17
17
14
14
10
10
7
7
7
7
7
3
3
3
3
3
3
30-Day Study
Average
Concen-
tration
(P8/1)
1
<1
23
2
19
<1
1
2
<1
1
<1
3
3
<1
<1
1
<1
<1
<1
<1
<1
<1
<1
12
1
<1
1
Maximum
Concen-
tration
(PR/D
5
1
660
21
220
7
17
59
4
12
2
33
60
6
4
24
2
8
1
1
4
1
1
350
36
4
28
Minimum
Concen-
tration
(Pg/1)
1
1
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Percent
Occurrence
20
6
3
17
23
3
3
3
6
29
14
14
11
11
9
9
6
6
6
6
6
3
3
3
3
3
3
36-Day
Average
Concen-
tration
(W8/1)
1
<1
19
2
16
<1
5
2
-------
TAM.K 14,
n» m au-uA«, '.IU-IIAV, AMU cunmntu it-UAt SHIOKIIAK* ouutur rxiuitm c<«i I.UTAKT
Si«-l)jy Slmly Ill-lint Sluilv . J6-l»y
Hi M/ vit*'
l,l,l-h lililuiui'tlmie
I'llliM ul 1*1 W
Kl ky !>"'"'•»••
»k!lliyl<-iw llili.ii.k
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Till til' III:
Tdtltlmiirlliylem'
PriU * t li 1 u f <*|'l«?«w 1
Hi* n«* 1
1 , ] , 4, - T( i ill 1 u rulicn i«»c
1 ,2-Ulllll»lllll«.bii 1 1 i*l.N
U««~.J-»IH:;
1 I'MI* lilwi iilii'iui'i*.'
K in. i j«l In...
fh-iiMiy'
IJviMi imt«
IUU
to
UK)
til
IOU
IIIU
IUU
20
1.1
100
ino
u
0
too
100
too
IUII
II
too
IOO
100
IIIU
11
1011
*'l
lull
IUU
IUU
IIM)
IUU
0
III
1)
a
67
a
If
0
II
II
JSE;
2
2
.'4
1
II
t
bl.
a
ion
II
91
61
7
VI
61
3
20
10
47
30
iO
U
7
;
U
to
67
100
10
10
0
SI
0
1041
a
60
0
7
11
a
0
to
)
l
CuillCH-
lui/l)
4
i
II
4
>2
7
14
4
<|
40
6
1
1
1
10
2
t
MD
<|
1
2
51
21
11
i
It
NU
1
MO
100
MU
)
NU
tr
Cum tu-
4
j
It.
4
72
6
14
4
1
17
7
I
1
2
10
2
s
-------
TABLE 14. COHI'ARISON OF TIIK SIX-DAY, :IIM)AY, AND COHIIINF.II 36-DAY KKCONIIAHY EFFLUENT I'll I OR ITY POLLUTANT CONCENTRATIONS
U)
Six-liny Slmly
Puiimi'lci Occurrence
Tl I rhl 010 1 limrofflplhane
2,4-Dlmelhyl|>lieiml
Acenaiilhli'ne
Dl-n-octyl I'hlhalalr
Illmrthyl MiltuUli:
I'liiurene
2-rhloroplieiiol
1 , l-nirhlornelhylriir
4-NltropliPlKil
Bls(2-iiiletliyoxy)»fthnii<'
AriMiaplithylene
1 , 1 ,2-Ti titllornelhaiie
1 , 1 1 2,2-Tvt racliluroelliaiifi
2-Nlli«|>h
-------
The secondary sludge solids concentration and the priority toxic pollutant
analytical results were much more consistent than those of the primary sludge.
During the combined 36-day study, six metals plus cyanide were detected 100
•percent of -the time and lead was detected 97 percent of the time in the
primary sludge. The only organic pollutants detected in the secondary sludge
at significant concentrations during the study were toluene and bis(2-
ethylhexyl)phthalate. Average metal concentrations for the six-day and 30-day
studies also reflected the priority pollutant metals' tendency to concentrate
in the sludge.
INFLUENT VARIABILITY ANALYSIS
An evaluation was undertaken to describe the influent data sets during the
six-day and 30-day studies and to assess whether these data are comparable.
The purpose of this evaluation is to determine whether the initial six-day
influent pollutant concentrations are representative of the long-term influent
pollutant concentrations. Summaries of percent occurrences (as discussed in
the previous-section),-means, ranges-and^standard-deviations were compiled to
accomplish this objective. It should be noted that no major changes in the
industrial dischargers tributary to the treatment plant or the characteristics
of their wastewater which would impact this analysis were known to exist.
Table 15 presents: 1) a more detailed comparison of the influent variabil-
ity for the 30-day and six-day studies for priority pollutants detected at
least 50 percent of the time during the combined 36-day period; and 2) a
comparison of the variability of the conventional parameters biochemical-oxygen
demand (BOD5), and total suspended solids (TSS). Mean values generally compared
well. For example, the six-day and 30-day average concentrations for benzene
(14 yg/4 and 18 Ug/£), chloroform (77 ug/fc and 73 ug/fc), ethylbenzene (20 vg/fc
and 23 ug/fc), bis(2-ethylhexyl)phthalate (14 ug/£ and 12 ug/fc) and chromium
(226 ug/i for both periods) are very similar. Of further interest is the
dispersion of the separate data sets around the respective mean values as
described by the standard deviation. For example, ethylbenzene and chromium
had similar mean concentrations during the 30-day and six-day periods. However,
the ..lower standard deviation for ethylbenzene clearly demonstrates that the
repeatability of the ethylbenze concentrations is much more probable.
The coefficient of variation, which is defined as the ratio of the pollu-
tant standard deviation to the mean concentration, presents a relative compar-
ison of pollutant distributions. The lower the coefficient of variation, the
narrower the data distribution. Higher coefficient values indicate a wide
distribution of the data. During the 30-day study, the coefficient of variation
was greater than one for 15 of the 26 toxic pollutants detected in the influent
50 percent or more of the time. This may have been due to highly varied pollutant
concentrations in the influent.
The six-day data compare quite well to the 30-day data. Of the 26 toxic
pollutants listed in Table 15, the concentrations of all but five pollutants
(phenol, 1,2,4-trichlorobenzene, naphthalene, copper and cyanide) from the six-
day -study were within one standard deviation of the mean concentrations for the
30-day study. Cyanide was the only parameter that showed a wide-spread differ-
ence between the 30-day and six-day studies. Analytical interferences present
during the six-day study are suspected as having caused this discrepancy.
44
-------
TABLE 15. INFLUENT VARIABILITY ANALYSIS
Parameter(l)
Volatiles
Benzene
1,1, 1-Trichloroethane
Chloroform
1 , 2-Trans-Dichloro-
ethylene
Ethylbenzene(2)
Methylene Chloride (2)
Toluene (2)
Trichloroethylene
Tetrachloroethylene
Acids
Phenol
2,4-Dichlorophenol
Base/Neutrals
1 , 2 , 4-Trichlorobenzene
1 , 3-Dichlorobenzene
1 ,4-Dichlorobenzene
Naphthalene
Bis(2-Ethylhexyl)
Phthalate
Di-N-Butyl Phthalate
Diethyl Phthalate
Phenanthrene
Metals
Chromium
Copper
Cyanide
Mercury (ng/ 1 )
Nickel
Silver
Zinc
Conventional
BODS
TSS
30 -Day
Mean
(WS/O
18
20
73
1
23
88
321
26
52
201
5
17
2
5
11
12
5
4
1
225
77
83
303
73
5
332
303
232
Study
Standard
Deviation
(ws/0
12
49
36
1
18
86
325
51
87
155
7
22
6
8
11
15
14
8
2
527
25
84
270
76
2
164
115
93
Six-Day
Mean
(WS/l)
14
43
77
2
20
40
378
10
81
448
2
100
1
4
55
14
4
6
3
226
123
4747
333
98
21
486
435
327
Study
Standard
Deviation
(V*/D
8
49
59
1
17
30
236
12
52
209
2
45
1
3
45
7
2
3
1
160
24
1664
816
37
7
132
112
95
1 Influent variability analysis conducted on priority toxic pollutants detected
50 percent of the time or greater in addition to lead and cadmium for combined
36-day period.
2 Outlier values were removed from data base.
45
-------
ESTIMATED POLLUTANT LOADS FROM INDUSTRIAL SOURCES
The influent wastewater pollutant loads were monitored on a daily basis
throughout the combined 36-day period. Table 16 presents the summary of the
day of the week average influent pollutant loads for priority toxic pollutants
'detected in the influent waste stream 50 percent or more of the time as well as
the averages for BOD5 and COD. Because the influent waste stream includes
combined sewer flow resulting from storm events, several daily loads were
omitted so that the day of week averages would not be distorted. For example,
on February 11, 1981, the lead load was omitted due to an increase by an
approximate factor of 12 caused by the combined sewer flow.
Data presented in Table 16 indicate that the majority of the priority
toxic pollutant loads occur Monday through Friday. Some loads occur in a
well-defined pattern throughout the week, but most do not exhibit any particu-
lar weekday trend. Figure 3 is an example of the daily variation in the mass
load to the MBWWTP.
In order to estimate the percent of industrial contribution per pollutant,
the average Sunday loads for each pollutant were assumed to represent the
combined residential/commercial contribution. -Realizing that a limited number
of industrial processes discharge to the MBWWTP on Sundays, the industrial load
based on this assumption is conservative. The estimated percent industrial
contribution was calculated by subtracting the residential/commercial contribu-
tion (average Sunday loads) from the average weekday loads and then dividing by
the average week day loads. The calculated estimates are comparable with the
available data provided by the MBWVTTP personnel. The industrial contribution
of 65 percent BOD5 coincides exactly with MBWWTP's records, while the 68
percent COD contribution is.comparable with the 75 percent value noted by
MBWWTP.
Other pollutants for which data are available for comparison are: cadmium
(66 percent for the 36-day study versus 88 percent from the MBWWTP records);
chromium (87 percent for the 36-day study versus 95 percent from MBWWTP re-
cords); copper (61 percent for the 36-day study versus 57 percent from MBWWTP
records); cyanide (71 percent for the 36-day study versus 57 percent from
MBWWTP records); lead (48 percent for the 36-day study versus 86 percent from
MBWWTP records); ^mercury (62-percent .for-.the 36-day study versus 85 percent
from MBWWTP records); nickel (69 percent for the 36-day study versus 94 percent
from MBWWTP records); silver (86 percent for the 36-day study versus 73 percent
from MBWWTP records); and zinc (69 percent for the 36-day study versus 61
percent from MBWWTP records). The industrial mass loading for total metals was
about 70 percent. With the exception of cyanide, most comparisons are close.
As previously mentioned, the percent industrial contribution for the 30-day
study is conservative since it is based on the assumption that no industrial
discharges occur on Sunday.
Extending this industrial pollutant calculation to organic pollutants, the
total industrial volatile organic contribution averaged 54 percent (ranging
from 84 percent for tetrachloroethylene to 35 percent for 1,1,1-trichloroe-
thane); the acid extractable organic contribution averaged 30 percent; and the
base/neutral extractable organic contribution averaged approximately 76 percent.
46
-------
TAHI.i: 16. DAY OF TIIK WKKK AVKRACK INFLUKNT I'Ol.l.UTANT LOADS FOK THK NUWVM'
- - • - — • • — ••
Vuliitj les
1,1, 1 -Tri I'll lo reel ha ne
Chloroform
1 , 2 -T i a us -1) ichloroelhy lene
Kthy I benzene
Me thy lene Chloride
Tel rai'liloroelliy 1 cut-
To IIIPIIO
Tr ichloroelhy lene
Ac ids
i'henol
2 , 4-l)i cliloi ophenol
Itase/Neulrals
1 ,2 ,4-Tri< liiorobeiizene
1 , 3-Hiclilorol>en/rne
1 ,4-l)ichloiot><>M2eiie
Naphthalene
bis (2-ElhyIhexyl) fhlhalate
IH-N-Butyl rhlhalale
Ilielhyl Phllia Lute
I'heuanl hrenc
Mela Is
Cadmium
Chroiniiim
Copper
Cyanide
Lead
Mercury
Nickel
y i | ve r
7. iiu
Convent ion.i 1
111)1)
TSS
. - -^ ... ..
Monday
4 1
4.5
40
1.3
9.7
20
17
103
21
85
1.1
16
0.82
2.2
4.6
13
0.56
0.29
0.30
4.2
58
34
21
25
3.2
161
144,500
279,600
._ . .
Tuesday Wednesday
11
4.6
42
2.3
13
26
28
113
5.3
84
2.6
It
1.4
0.81
9.0
2.2
0.97
1.5
0.15
3.1
90
45
26*
26
0. 16+
25
3.4
146
135,600 158
267,600 314
11
4.1*
36
2.2
7.7
32
17
103*
17
95
2.5
13
0.95
1.9
14
2.9
1.4
3.3
0.31
2.0
60
45
21*
36
0.26+
96
4.7
209
,600
,100
POUNDS
Thursday
10
4.5
37
2.1
14
30
28
332
3.7
147
4.3
21
0.74
6.0
8.1
1.9
5.2
1.7
0.71
2.6
79
38
37*
24
0.14+
48
8.9
157
163,800
348,800
Friday
5.1
2.5
23
0.86
10
24*
19
96
3.9
72
0.72
11
1.1
2.3
7.6
4.0
1.9
3.0
0.56
1.5
63
29
56'-
19
0.16+
31
3.7
121
103,800
232,700
Saturday
3.7
4.0
14
0.95
3.2
25
7.1
96
9.6
70
1.2
6.0
0.22
0.74
3.9
4.0
1.9
1.6
0.64
1 .3
52*
26
8 . 9*
18
0. 12 +
14
1.9
82
99,570
181,500
Sunday
4.3
2.6
7.1
0.66
4. 1
15
3.4
84
2.7
68
2.3
1.0
0.39
0
3.6
2.3
0.69
0.44
0.12
0.90
9-0
15
12
13
0.07 +
14
0.64
49
49,600
90,370
Weekday Ksli
Average Load
8.2
4.0
36
1.7
11
26
22
149
10
97
2.2
14
1.0
2.6
8.7
4.8
2.0
2.0
0.41
2. 1
70
38
40
25
0. 18+
45
4.8
159
141,300
288,600
mated Industrial
ing Conlribnt ion( 1 )
48%
35%
R0%
62%
63%
43%
84%
53%
73%
30%
47%
93%
61%
100%
58%
52%
66%
77%
70%
66%
87%
61%
71%
48%
62%
69%
86%
69%
65%
68%
(I) Kui weekdays - Monday through Friday.
Outliers li.ivf been removed from Lhe data base.
» V,11 ucs are 10 ' pounds
-------
90 r-
Co
AVERAGE WEEKDAY LOADING « 36lbi/DAY
BASELINE DOMESTIC LOADING < 7.1 Ib./DAY
2/io/ei - 3/ii/ai
FIGURE 3. DAILY CHLOROFORM MASS LOADING GRAPH
-------
TREATMENT REDUCTION OF PRIORITY POLLUTANTS
Treatment efficiencies for selected conventional and non-conventional
pollutants and for priority toxic pollutants were calculated for the six-day,
30-day, and 36-day studies. Tables 17, 18, and 19 summarize the analytical
data for the combined 36-day study, the 30-day study, and the six-day study,
respectively; calculated percent removals are presented for each study. For
this evaluation, daily concentrations recorded as less than the detection limit
in both the influent and effluent were assigned a zero value; zero was used as
a data point in calculating average values. The daily percent removals presen-
ted in Appendix C were calculated using zero for influent concentrations less
than the detection limit and the detection limit for secondary effluent concen-
trations reported as less than the detection limit.
Table 20 presents the mass pollutant removals for the conventional pollu-
tants BOD.5 and TSS; for the toxic pollutants lead and cadmium; and for the
priority toxic pollutant compounds detected in the influent over 50 percent of
the time during the combined 36-day study. Influent, primary effluent, and
secondary effluent concentrations reported as less than the detection limit
were assigned a zero concentration; zero was used as a data point when the
average values were calculated.
As shown in Table 20, volatile organic pollutant removals through primary
treatment ranged from 42 percent for trichloroethylene to no reduction for 1,2
trans-dichloroethylene and ethylbenzene. Generally, volatile organic pollutants
were not reduced as a result of primary treatment. The activated sludge
process significantly removed the volatile organic pollutants from the waste
stream. These compounds were not notably concentrated in the waste activated
sludge. These observations suggest that volatile organic compounds are either
air stripped or biodegraded during secondary treatment. Secondary treatment
percent removals varied from 100 for 1,2 trans-dichloroethylene to 47 percent
for methylene chloride.
The acid extractable organic compounds (phenol and 2,4-dichlorophenol)
were not significantly removed during primary treatment, but were reduced by 92
and 46 percent, respectively, through secondary treatment.
The base/neutral extractable organic compounds were present at very low
concentrations in the influent. Several of these pollutants [1,2,4-trichloro-
benzene, naphthalene, bis(2-ethylhexyl)phthalate, phenanthrene, pyrene and
fluoranthene] exhibited an affinity to concentrate in the primary and WAS.
These pollutants may be removed from the wastewater by accumulating or prefer-
entially adsorbing (in the case of hydrophobic compounds) onto settleable or
floatable solids. The secondary removals for base/neutrals ranged from 92
percent for naphthalene to six percent for di-n-butyl phthalate. Pesticides
were not detected in any of the waste streams throughout the 30-day period.
With the exception of chromium and nickel, which showed minimal removal as
a result of primary treatment, the primary system removal efficiency for the
priority toxic pollutant metals was approximately 20 percent. Metal primary
treatment removals were not of the expected magnitude. The expected primary
treatment efficiency for suspended solids was also low with a removal of only
49
-------
IK AC 11 OH
CUNVENflONALS
HOH-COHVEH11OMAL 8
WOLATUFS
Ul
o
AC 11 EXTRACT
TABLE 17
SUHMAKT Of ANALYTIC*! HAJA
CIIAriANIIUOA 4-l>AY AND JO-HAT SlUHltfi COMUNttl
PAHAMtltR
IOIAL SUSP • SOLIDS
COD
OIL 1 OKIA3C
>
TDIAL PIICHOLI
IOIAL SOLIDS
IOIAL OIBS. SOLIDS
UNITS
fOIAL V0LAIUE SOL I PS
VCHAMU MSB. SOL I US
IOJAL VOL. DUB. SOLIDS
AHHOHIA HllfcOOEN
IOC
MH2EHC
CARIiON TCTftACIILORIDE
CIILOhOtCNItNE
«l>l-TfilCJflOftD£THAME
il-DICtlLOnOETHANE
, 1.2'IRICIILOROEIHAHE
>l>2>2-ICIRACMLOflOCriMNE
IILOKUE IHANE
IILOHOFORN
. I-PICMLOKOEIHTIEHE
• 2-1RAHS-DICHI OROETHTLENC
, 2-MCIUOROf ROPAHE
/3-KICMI OROPKDPYLENE
ETHTL*EHZENC
HE1HYLENE CttlOHiDE
HETIITL Cl<( OKI DC
P ICHL OR 0» KiO»OHC T HANE
TR I COL DROFLUOKOnE THANC
PICHlOROftlHUOKOnEIMAHE
CHLORODIkROnOni'TIIANE
TCTRACHLOKOCTNrLtME
TOLUENE
TRICHLOROETHYLENE
VINYL CHLOftlliE
2f4.4-TftfCM4.0M)fHEMUL
MMtill OfcOBE 1 A CUE SOI
2-CHLIIfiOFHEHOL
2r4-DINETIin>IIENUI.
2-HltkanttNtH
4-HUKOFHEIim
2.4-PINITKOHIEHOL
PtNIACHI-OROMIENOL
PKCKOL
fOLLUTANia HUT LIUICD WERE NEVER
1-tEES THAN (HAX. CEtfCIIOH LIMIDI
N-e WOT ['ETCCTEP.
INFLUENT
no/L
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
NL/L
HO/L
HO/L
no/i.
NO/L
MO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UQ/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/l
UO/L
124
24*
441
20
7*3
11*4
VIS
*
13B
IOB
I5B
14
23*
17
<
(
<
4
< T
<
<
L
74
<
<
23
Bl
10
L 1
< 1
N-D
< 1
57
33ft
23
1*
< 1
< 1
< 1
3
2
H-D
1
•'. 1
2
244
SECONDARY
trnuENT
45
34
I4S
4
114
*33
BB4
1
144
I4B
24
14
40
4
N-D
1
H-P
3
H-P
1
1
H-D
34
1
1
H-P
H-P
4
72
N-D
1
1
N-P
H-P
4
34
4
N-P
1
1
1
3
3
1
1
N-P
1
37
rctii
ftEN.
B4
• 4
75
• 4
B3
22
1
»4
91
21
•3
IB
75
7*
-
70
-
• 1
-
33
7-7
• '• .
32
«4
0
-
-
•1
12
-
-
43
-
-
a*
64
04
*
20
SB
»1
44
-
-
-
-
73
83
f-MHAKY
EFFLUENT
2*7
174
5V*
27
634
1134
*3B
3
202
1*0
104
19
21*
14
< 1
< 1
N-0
21
< 1
4
N-P
N-P
72
< 1
1
N-D
N-P
2*
B4
2
H-D
< 1
H-D
N-D
44
343
14
•: i
< i
< i
< i
4
3
2
N-0
•' 1
2
242
fRINAfiY
BLUDOE
10*04
23110
40341
347B
1242
280*7
1783
*M
14003
734
144*7
24
3372
14
N-D
4
4
BO
17
93
< 1
N-D
42
N-D
13
N-D
N-D
120
2*
N-D
< 1
< 1
I
H-ll
103
77*
32*
< t
N-P
N-D
N'D
N-D
N-D
N-P
N-D
H-D
< t
211
SECONDARY
SLIH'UE
4114
41 70
HOI J
4(13
IBi
4B»4
147
13*
4444
JI4
427*
13
1334
j.
M-[,
< 1
H-D
3
H-P
< 1
H-D
< 1
17
U-D
II -I'
H-D
H-D
(1
;i>
II -U
!»-!•
H-D
< 4
I»-H
12
113
»
U-D
II- D
H-D
U-D
M-P
|4~P
rt-D
II
'V-D
4
4
<'LEBB THAN
-------
TABLE 17
SUMMARY OF ANALYTICAL DATA
CHAIIANOOOA 4-DAY AMD 30-HAY STUDIES COMBINED
FRAC1ION
BASE-NEUTRAL8
PESTICIDES
METALS
PARAMETER
ACENAPHfHENE
BCNMDINE
I r2r4-TRlCHLOR08EHZENE
HEXACHLORO»ENZENE
HEXACHLOROETHAHC
2-CtlLORONAPIUHALENE
I>2-DICHLORO»EN2ENE
1.3-PICIILOROBEN7EME
1>4-DICHLORO»EN»NE
2>tf-OINtTROTOLUCNE
l>2-T)IPHENYLHYDfcAZlNE
FLUDRAHTHEHE
4-CHLOROPHENYL PHEHYL ETHER
IIS(2-CIILOROISOF'ROPrL) CTHER
BI8l2-CMlOfiOETHYOXr> ME THANE
1BOPKOROHE
NAPHTHALENE
N-HI IRQSODIPHENYLAHINE
N-HITROSODl-H-FROPYLAMINE
BIS42-EIHYLHEXYL) PHTHALATE
tUTYL BENZYL PHTHALATE
&I-N-BUTYL PHTHALATE
DI-N-OCTYl PHTHAUATE
til ETHYL PHTHALATE
DIMETHYL PHTHAtATE
1>2-BENZANTHRACENE
BENZQ (AIPTRENC
1 1 > I 2-BENZOFLUORANTHENE
CIIRYBENE
ACENAPMTHYLENE
ANTHRACENE
FLUDRENE
HIEMANrMKEME
IMDENOC! r2»3-C»D> PYRENE
PYRENE
ALr-HA-EHIiOSULFAN
ALPHA-bMC
OAHHA-bllC
ANTIMONY
ARSENIC
BERYLLIUM
CAOHIUn
CHROMIUM
COPPER
CVANIPE
LEAD
MERCURY
NICKEL
UNITS
WO/L
UO/L
UO/L
UO/L
UU/L
UO/L
UO/L
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UD/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
NO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
INFLUENT
14
H-D
11
H-D
H-D
< 1
N-D
1
2
S
N-D
< 1
< I
N-D
N-P
N-D
IV
H-0
< I
11
< 1
S
< 1
3
< 1
2
H-D
N-D
<
<
«
^
H-0
N |
104
124
144
4
4
< 1
9
224
as
883
43
309
79
SECONDARY
EFFLUENT
2
N-B
7
N-B
NO
N~D
N-D
< 1
1
< 1
N-B
N-D
< 1
N-D
H-D
< 1
N-D
J
N-B
N-D
10
< 1
2
I
S
2
H-D
N-B
H-D
N-D
< 1
N-D
< 1
< 1
H-D
L 1
L 1000
L 1000
39
1
2
L 1
1
49
19
97
13
17
44
PCHT
REM,
90
-
79
-
-
-
-
37
37
87
-
-
84
-
.
96
-
90
.
-
24
74
67
-
-
-
-
-
-
-
84
-
88
93
-
-
-
-
77
49
40
-
47
78
7B
90
47
95
41
PRIMARY
EFFLUEHT
II
< 1
27
-: i
H-D
< 1
< |
2
2
3
N-D
< 1
< 1
N-D
< |
2
< 1
22
< t
< 1
13
-'. I
3
2
0
1
N-D
N-D
H-D
< I
< 1
< t
< 1
t
N-D
-: i
N-D
L 1000
104
3
3
< t
4
232
68
492
41
147
74
PRIMARY
SLUIiOE
13
N-D
1134
N-D
1
N-B
N-D
S3
22
44
2
N-D
194
3
N-D
N-D
N-B
404
N-D
N-D
IS29
100
73
4
31
N-D
41
24
24
47
4
97
44
189
4
127
N-D
2
N-D
92
444
71
173
13225
7431
8134
3821
34501
4O74
iiECONBARY
IILUDOE
If-D
H-D
V9
H-D
H-D
II-V
H-D
;>
H-D
H-D
H-0
tl-D
:15
II-D
N-D
.i-r
N-D
40
N-D
N-D
194
26
9
N-II
N-0
N-D
4
N-D
1
3
2
3
N-P
2
H-D
3
N-D
N-ti
N-D
19
120
24
44
3349
1224
374
747
IBAI
720
(OlIUIflNTS NOT LISTED WIRE HEVtR DETECTED
L-irSS IMAM (MAX. nETECIION L 1 (II I ) I <*LES9 THAN (AVERAGE CONCEM1RATI ON»I
N-t'-NOr I'trtTTLH.
-------
TABLE 17
Of ANALYTICAL |IATA
CHATTAHOOUA *-»Ar AMfi 10-DAY STUDIES CONklNC*
FRAC IIUN
HtlAl*
WIN-CONV, MtMI.8
PAftANEIER
SllCNIUM
611 VEd
UHIIB
INFLUtHT
t fCNI
EmuEHr REN.
PftiHAfcY
cmvEftr
PKlHAftY
BLUDOf
Z1HC
kAK I UN
tOKUN
CAlClUlt
COIALf
IRON
HAUNCSIUM
HANOANE BE
NOLtr»t>CNUH
saviun
TIN
IIIANlUn
VANAMUn
YTTRIUM
UO/I
UflVL
UO/t
ua/t
UO/L
UO/L
UB/L
no/L
UO/L
UO/L
NO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
< I
B
'. I
121
11*
47
14
3200
281
7
29)
II
22
S
II
< I
I
< I
«09
10
12*
44
II
444
201
4
23R
* •
IV
< I
L 9
44
•5
19
99
ft
9
7
20
A
10
SO
IB
II
»*
94
I
14
I
29V
910V
107
112
47
I*
294*
I
200
253
f
21
3
10
7
L 170
NOT RUN
NOT RUN
NOt RUN
NOI RUN
NOT RUN
, NOT RUN
NOI RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUM
NOI RUN
NOT RUN
NOT RUN
SCCONBARY
BIUPOE
I
IV*
SO
3042
NOT RUN
NOT RUN
NOT RUN'
NOT RUN
NOT RUN
NOT HUM
NOT RUN
NOT RUN
NOf RUM
NOf fct/N
Nor RUM
NOr RUN
NO I RUN
NOf RUN
M
POLIUIANTB N(IT II9TEU UffcC NCVfK fitTECICP
1'IEBS IIIAN InflK. tittCCUOH linilll '-LESS
N ti'NOI t.tTltUli.
THAN (AVERAOC CONCENTRATION!»
-------
TADLE 17
SUHHAkt OF ANALYTICAL DATA
rilAITANOOIIA 4-DA1T AMD 30-DAY STUDIES COMBINED
ADDITIONAL SAMPLE POINTS
FRACTION
CONVENTIONALS
MOH-CONVENT IOHALS
PARAMETER
•00
TOTAL SUSP.
COD
OIL I GREASE
SOLIDS
TOTAL PMEH018
TOTAL SOLIDS
TOTAL HISS. SOLIDS
SETTLEAIIE SOLIDS
TOTAL VOLATILE SOblDS
VOLATILE HISS. SOLID!
TOTAL VOL. SUB, SOLIDS
AMMONIA MITROOEN
TOC
VOLATILES IENZENE
CHLOROBCMIENE
111 > I - IRICIILOROE THANE
Itl-OICHLOROETHAME
CHLOROETHANE
CHLOROFORM
I»2-TRANS-D1CHLOROETHYLENE
CTHYIIENZENE
HETHYLENE CHLORIDE
DICHLOROBROMOrtETHANE
TRICHt.OROFLUOROHETMANC
CHIORODIDROMflHE THAME
10LUENE
VINYL CHLORIDE
ACID EXTRACT 2i4ti-TRICHLOROPHEMOL
FARACHtOROHEfA CRESOL
2-CHLOROPHEMOL
2.4-DICHLOROPHEHOL
2.4-DIHETMYLPHENOL
FENTACHLOROPHEHOL
PHENOL
BASE-NEUTRALS ACENAPHTHENE
I>2>4-TRICHIOROBEMZENE
ll3-DICHLORO»ENZEHE
lt1--DICHLORO»EMZENE
lt4-DICMLOKO»ENZENE
ItJ-DIPHEMVLIIYIIftAZINE
FLUORANIHENE
•IB<2-CHLOROETHYOXYt METHANE
NAfHIHALENE
NITRODENZENE
N-NIIROBODII-HENYLAHINE
»IS<2-ETHYLHEXYLI PHIHAtATC
POIIIMANTB NOT LISTED UEftE NEVER DETECTED
I.-LESS THAN
-------
NCUIRALI
HCIALS
MUM-COHV. METALS
TABLE 17
6UHMART Of AMALVI1CAL PAIA
CIIATIAHOOOA 4-DAV AHP IO-OAT 0TUt>IE6
ADDIT10HAL SrtMfLC POINT!
PAAAHETER
*ur,»L trMm PHTMALATE
OI-H-HUTTL PIITHALATE
PI-N-OCfTL PHTHALATE
PIETHTL fHTHALATE
lf2-IEHZAHTHflACEHE
CHRlfl£HE
ACEt»APHTHYLEN£
ANTORACEHE
HIENAHTMRENE
1 1 2 1 »• 4~MfcENZANTIIftACeME
PYKCHE
CNPK1M ALOEtmiE
PELTA-liHC
AM 1 1 HOMY
AKSEHtC
CAtiHIUH
CHkfHIlUn
COPPER
LEAP
HEkCUAY
NICKEL
SEICNIUH
SILVER
THAlLIUtl
2 INC
ALUMINUM
MftlUM
IOKON
CALCIUM
COPALI
IRON
HANOAMESE
HOLYHDENUn
SOPIUH
tlH
T1TAMIUM
VAHAHIDH
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
HO/I
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
liO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
VACUUH FILM
FILTRATE
N-P
1
1
10
M*P
< 1
S
2
N-P
t
2
N-P
< 1
N-P
N-P
< 1
4
L 1
3
120
88
440
73
333
9?
< t
S
< 1
114
3013
171
144
234
11
3117
10
1822
L 14
237
IS
7
1
IB
IR PIOESTER
SUPERNATANT
3
7
12
10
1
< 1
N-P
3
1
4
y
1
2
2B1
21?
3
43
I
22
843
72?
11
348
4217
ISO
4
74
2
2170
1448)
f 11
22S
114
»4
23333
42
2*21
If
234
44
111
11
1»Q
TAP
HATED
M-ti
1
2
L t
N-P
N-P
H-P
H-P
N-P
H-e
H-D
H-P
H-D
H-D
H-D
< I
< 1
L 1
2
3
12
f
14
1300
2
< 1
< t
L 10
30
41
22
L 20
23
11
42
4
1
L 33
B
10
12
< 1
L 3
KU.LUfA»I8 Hill LISrEH Ulfll NEVER HEIECIEP
I-LESS fHAH (MAX. PETECIION UhMU <-LES3 THAN (AVERAOE CONCENIRAI ION»
N-P'MOI l>ETECr£[i.
-------
TABLE IB
or ANALYTICAL KATA
TRACTION
CONVENTIOHALS
NOH-CONWf NtlOHAtS
VOLAI1LEB
Ul
ACIP EXTRACT
CHMTANOOOA 30-DAY STUDY
FARAHETEfi
>OD
tOTAL SUSP, SOLIDS
COP
OIL t ONEA3E
TOTAL PHI HOLS
TOTAL SOL I US
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLID6
VOLATILE DISS. SOLIDS
TOTAL VOL. SUS. SOLIt'S
AMMONIA NITROGEN
TUC
DENZCNE
CAFPON TttRACHLORIDE
1.2-DICIH OROETHAME
lil>l-TRJCMLOROETHANE
lil-DICHLOROETHANC
1,1.2-TRICHLOROE THANE
I > 1 1 2 1 2- TETRACIILOROE1 HANE
CM1.0ROET«ANE
CMLDROFOF.H
1>1-DICHLOROETHYLENE
li2-TRANB-DICHLOROETHYLENE
1,2-PICMLOFOPROPANE
1 .3-PICHLOKOFKOFYLF.HE
CTHYLtENrCNE
HETHYLENE CHLORIDE
HETHYL CHLORIDE
IRICHLOROrLUOROHCTHANE
CIILOROD I »KOHOHE THANE
rETRACIILOfcOETMYLEME
fOLUENC
tRICHLOROETHYLENE
VINYL CHI OR Hit
2.4i4-TRICMLOROFHENOL
PARACHLOROHETA CREBOL
2-CHLOROFHENOL
2t4-PICHLOROPHENOL
2.4-H1HITHTVPHENOL
2-HITfiOF'MEMOL
4-N1TROF-HENOL
2>4-DlNITROFHENnL
t-ENrACIILOkOF-HENOL
ACENAPHIHL'NE
I'C.SE NCUTKrtl S
FUI.IUIANIS NUI LISTED UtKE HEVLR PEIECTED
1'IF.SS THAN (HAX. DETECTION LIHITM <-LE8S THAN IAVERAOE CONCENTRAT ION)»
M-n^NOt PEIELTED.
UNITS
HO/L
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HB/l
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UD/L
UO/L
UO/L
,UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
IHFIOEMT
303
232
37B
27
743
1128
874
334
184
190
IS
230
IB
< 1
C 1
< 1
20
< I
< 1
< 1
N-0
73
3
< 1
< |
i I
13
87
12
< 1
< 1
32
321
24
23
< 1
< |
< 1
4
2
N-D
1
< 1
2
201
17
N-D
SECONDARY
EFTLUENT
34
33
134
7
77
8B7
833
140
137
24
7
tt
4
N-D
< 1
N-0
9
N-D
< 1
< i
N-D
37
< 1
N-D
N-0
N-D
4
82
N-D
< 1
N-D
7
34
4
N-D
< 1
< 1
< 1
3
3
< 1
2
N-D
< 1
40
2
N-B
f CNI
KEN.
88
84
74
73
87
21
S
S3
27
84
38
73
70
-
40
-
75
-
34
78
-
47
74
-
-
-
61
B
-
47
-
84
83
84
-
_
37
73
47
-
-
-
-
73
80
72
-
F-RIHARY
EFFLUENT
207
144
352
24
773
1087
723
283
184
77
IS
223
17
< 1
< 1
N-0
21
< 1
7
N-D
N-P
77
•: i
1
N-0
N-D
32
77
2
•; i
N-0
47
337
18
< 1
< 1
< 1
< 1
7
3
3
N-D
••: i
< I
232
13
< 1
F-RIHARY
8I.UPOE
7720
21447
33847
2534
1183
22.803
1147
12704
33S
12343
24
3723
13
N-D
< 1
4
74
7
43
< 1
N-D
47
N-D
•: 1
N-D
M-D
43
21
N-D
N-D
N-D
31
SIS
137
•'• '
N-P
N-D
N-P
N-D
N-D
N-D
H-l»
N-D
X 1
223
14
N-P
SECONDARY
SLUtiOC
2825
4382
12107
331
1'JO
7313
733
4434
IS!
4503
IS
1332
2
N-D
-r i
N-D
4
H-P
< I
N-B
< 1
18
N-D
N-D
M-P
N-P
7
33
N-P
N-P
N D
JO
B4
4
H-P
N-P
N-P
N-P
N-P
N-P
N-D
13
N-P
5
N P
N P
N P
-------
TABl.K 18
SUMMARY 01 ANAIYIICAL I'AIA
CHAMANOOOA JO-UAY itUUY
FRACTION
*ASE-NEUIRAL8
HI I ALB
PARAMETER
I , 3 • 4 - I R ICHL OROIENZE HC
IIEXACHLOROtENZENE
IIEXACMLOAOETII4HE
IU8<2-CHlOROEJilVL> EIHER
2-CIILORONAP HTHAI EME
Ifl-DlCHLOfcOtEMZCNE
1.3-DICHLORDtCHZENE
1 1 4-DlCHLOROfrENZeNE
2.4 biNiiKOTorufNE
1 1 2- DIPHEHYLHYDRAZINE
FlUORANTHEHE
4-CHLDROf'IIENYL PHEHYL CIIIEK
SI8(2-CHLOROISDPROPYL> ETHER
DIS(2-CHLOROEMIYOXYI HE I MANE
ISOPHORONE
NAPHTHALENE
N-HITROSODIPHEMTLAHINE
N HITR080DI-N-PROPYLAH1NE
•I8I2-ETHYLHEXYLI PMTHALATE
DUTYl tENZYL rtlTHAlAIE
DI-N-DUTYL PHTIIALA1E
DI-N-OCITL FHIJIALMC
DIETHTL PIITHALAIC
DIMETHYL PHIMALATE
1>2-DENZANTHRACEH£
•ENZO (A)PYRENE
1 1 f 1 2- DENZOFLUOR AN THEME
CIIRYSEME
ACENAPHIHYLEME
AMIMRACENE
FLUOREHE
FHEMANtllRENE
iMDENO(l>2i)-r>(i> PYREHE
PTKtNt
ALfl(A-»MC
ANIIHOHY
ARSENIC
llERYLLIUM
CMKOHfUn
COPPER
CYANII»E
l£AI«
HERCUttY
NICKEL
SELCN1UN
SILVER
ZINC
UNI IB
UO/L
UO/L
UO/L
UO/L
UU/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
Ub/L
UO/L
UO/L
UO/L
UO/L '
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
«0/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
17
N-D
N-D
C 1
N-D
NO
3
4
N-D
', I
1
N-D
H-D
3
M-D
12
N-D
( 1
12
N-D
4
( 1
4
( 1
2
N-D
N-D
( i
C 1
c i
t
! 1
N-D
1
N-D
2
3
< 1
4
224
77
83
24
101
71
( 1
9
132
SECONDARY
EFFLUENT
4
N-D
H-D
M-D
N-D
< 1
2
< t
N-D
N-D
< 1
M-D
N-D
< 1
N-D
< 1
N-D
N-D
10
N-P
2
1
4
J
N-D
N-D
N-D
N-D
< 1
N-D
< 1
N-D
N-D
N-D
N-D
< 1
1
L t
2
91
21
80
9
20
IT
L 29
1
100
PCNI
REH.
42
.
-
-
-
_
34
04
-
-
04
.
-
*4
_
*4
-
-
20
-
40
-
-
. -
-
.
•
-
04
00
-
.
-
-
04
44
.
92
77
73
-
80
»3
47
.
01
70
PRIMARY
EFFLUENT
12
< 1
N-D
, 1
< 1
•: I
2
9
N-D
< 1
1
N-D
< 1
3
1
II
< 1
< 1
f
< 1
1
1
0
2
N-D
N-D
N-D
< 1
< 1
< 1
< 1
< 1
N-D
< 1
N-D
1
2
< I
1
22*
43
181
27
200
44
L 23
9
241
PRIMARY
9LUDOE
404
N-D
2
N-D
N-D
43
N-D
41
2
N-D
1*4
4
N-D
N-D
N-D
938
N-D
N-D
770
24
N-D
9
37
H-D
37
31
31
44
£
47
55
197
a
too
3
Tl
790
47
1*3
14740
7110
1010
490*
34348
4308
7
377
2SBB*
SECONDARY
SLUDOE
119
M-D
N-D
M-
N-
2
N-
N-
N- i
N-
17
N-
N-
N-
N-
44
N-D
M-D
ISO
33
11
N-D
N-li
N-D
4
N-D
4
2
I
N-H
I
N-D
4
H-D
1*
13V
23
74
4417
1300
183
787
1147
621
L 40
3*34
POLLUIANIS NOT LISIED HIRE NEVER DETECTED
L-LESS THAN I MAX, DETECTION LIHITH <>LES8 THAN (AVERAOE CONCENTRATION)!
N-lK-NOT DETECTED.
-------
TABLE IB
tUMMARV OF ANALYTICAL DATA
CHAtfAMOOOA 10-DAY STUDY
FRACTION
NON-CONV. MEMLS
PARAMETER
ALUHINUH
BARIUM
• ORON
CALCIUM
COIALI
IRON
HAONE9tUN
HANCANEBE
HQLTIDENUM
BOtiJUH
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/l
UO/L
NO/I
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
INFLUENT
939V
110
III
48
14
2»7»
•
101
i
731
17
9
12
SECONDARY
EFFLUENT
594
2?
»2
4«
II
411
I
217
4
31?
21
L 9
L 9
PCNT
REN.
TO
74
23
9
24
IS
4
28
27
-
-
-
9f
r-RIMART
EFFLUENT
48»»
100
111
48
14
2424
8
2T2
A
23?
18
1
12
PRIMARY
8LUOOE
NOT RUN
NOT RUN
NOT RUN
NOT RUN
N01 RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUN
SECONDARY
SLUDQE
NOT RUN
HOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
Ul
r-OI.LUTANTS N01 I Ifiltti WERE NEVER I'EIECTED
L-LEGS THAN (MAX. 1>EUCTIUH LINITIt <-LESB THAN (AVERAGE CONCENTRATION) I
N-l'-NOf
-------
TABLE 18
SllrtH/.M UF ANALYTICAL PA IA
CHATIANUOOM 30-PAT ilUHI
ADI'iriOMAL SMFLt
fit AC 11 ON
COMViNHOMM-S
NUH-CONVENI10NALB
vm.Atfl.C8
Ul
00
ACID
BASt
»pp
TOTAL SUSP. SOI IPS
COP
OIL I OREABE
TOTAL PHENOLS
TOTAL tiOLU'B
TtflAL PISS. 80L1PS »
TOTAL VOLATILE SOLIDS
VOLATILE PISS. SOLIDS
TOTAL VOL. SUS. SOLIDS
AnnONIA NIIKOOEN
IOC
at Hit HE
CHLOROtEHZEHE
1.1.1-IRICHLOMOETHANE
lll-DICHLOROEIHANE
CHLOROFOHH
I>2-TNAMS-PICHLOROEIHYLENE
E.THYLHENZENE
AETHYLEHE CHLORIPf
PICIILOftOftKOHOnE THANE
TRICHIOROFLUOROMETHANE
IOLUENE
PARACHLOftOHETA CRESOL
2-CHLOROPHENOL
2. 4 -0ICIH OROPHENOL
2.4-PinCTHVLPHENOI,
PHENOL
ACENAPHTNENE
1r 3,4-TfilCHLOftO»EMZ£NC
lrl-DICHLORO»ENZEHE
!r4-PICHLORO»EHIENE
lf2-PIPHENYLHYbKAZlNE
FLUORAMTHENE
»iai?*CHIORO£THirOXY> METHANE
NAPHTHALENE
HIIROBENZEHE
M-NITROSODIPHtNYLAHlNE
• IX2-EIHYLHEXYL) PHTHALATE
PI-N-IUTYL PHIHALATE
PI-N-OCTtL PHIIIALATC
DIETNYL fltlHALATE
I>2-»ENZANIHRACENE
CIHtYSENE
ACCNAPIITHYI.ENE
AHTHRACEHE
POLLUTANTS' NOT I IBTEP UEfcE NEVER MTECUIi
LM.ESS THAN (MAX. PETLCTION LINIIII <*iEfis THAN fAVERAGE CONCENT*AMON»I
N P-HOI PETECIEP.
OH III
HO/L
HO/L
HO /I
HO/L
UO/L
HO/L
WO/L
MO/L
MO/L
NO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UD/L
Uff/L
UO/L
UO/L
UO/L
UO/L
UO/L
UG/l
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
VACUUM FILTER
f ILlKATL
70
4*2
JI2
U
111
1042
1171
230
114
104
79
147
2
M-0
< 1
N-D
H-0
H-0
2
12
H-D
< t
•
H-0
< t
< 1
4
14
M-ti
N-D
2
< 1
2
< 1
2
12
M-0
H-0
14
1
4
II
H-0
< 1
9
2
PIOESTEft
SUPERNATANT
508
fll
UBS
• 2
I«9
2194
1432
030
312
910
»3
410
10
17
< 1
I
< 1
10
2AV
IS
H-0
< 1
14*
< 1
H-0
H-P
N-D
17
1
7
23
<
1
»
•T
N-D
i
TAP
WATER
L 1
1
L 23
2
L 3
110
117
47
47
< 1
L 1
4
3
•: >
< 1
H-B
It
H-P
4
»
1
< 1
9
H-D
N-D
N-D
N-D
M-lk
H-P
M-0
H-D
N-D
H-D
N-D
H-D
N-D
H-P
H-D
*7
1
3
H-P
N-D
H-P
H-D
N-0
-------
TABLE 18
SUMMARY OF ANALYTICAL DATA
CHATTANOOGA 30-DAT BTUtiY
ADDITIONAL BAMfLE POINTS
FKACIIOH
•ASE-NEUTftALB
METALS
PARAMETER
I.I2-BENZOPERYLENE
FLUOKENE
PHENANTHRENE
if2l3iA-I>IliENZANTMRACENE
f-YRENE
ANTIMONY
ARSENIC
VO
HOH-CONV. METALS
CADMIUM
CHROMIUM
COPPED
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
bORON
CALCIUM
COPAL I
IRON
HAONESIUM
MANGANESE
HOLYIAENUH
SODIUM
TITANIUH
VANADIUM
YTYRIUM
UNITS
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
MO/L
UO/L
UO/L
UO/L
VACUUM FILTER
FILTRATE
N-D
I
2
M-D
< 1
L 10
9
L 1
L 3
130
?4
12
il
«40
91
4
340
9404
172
170
203
13
3702
30
2130
L 10
2S4
4
4
44
DIOESTEfc
SUPERNATANT
1
3
S
1
< 1
2
32
1
II
312
340
31
2*2
24iO
212
14
1104 .
23200
330
IB*
204
3*
13424
37
2732
13
21V
37
20
201
L
L
L
L
L
L
L
L
L
L
L
L
TAP
WATER
N-D
M-0
N-D
N-D
N-D
23
10
1
3
4
II
1
SO
300
30
1
33
31
22
20
23
1
to
4
2
10
6
39
3
3
POLLUTANTS NOT LISTED UERE NEVER IiETECTED
L-ltSS THAN (MAX. I'tftCUON IIMITU ->LESS THAN (AVERAGE CONCENT RAI! OH M
N It-Nil!
-------
TABLE 19
SUHHAftY OF 6HALYIICAI IMIA
CHAT1AMOOQA 4-OAY SIUUY
FRACTION
CUNVENIIOHALS
WON-CONVENT IONALB
ON
O
EXIRACT
liASE-MEUIfiAlS
f-ARAHEIER
HUD
TOTAL SUSP. SOLIDS
COD
OIL I OREASE
TOIAL PMEHOLS
10Ml SOLID*
TOTAL bISS. 601 IDS
SEIILEAILE SOLIDS
TOIAL VOLATILE SOLIDS
VOLATILE DI88. SOLIDS
TOIAL VOL, SUS. BOLIDB
AMMONIA NITROOEH
TOC
VOLAIILE8 MMiENt
CHLOROIENZEHE
1.1.1-TRICHtOKOETIIANE
Itl-DICHLOROETHANE
CHLORUI--ORH
I»2-TRANS-OICHLOROCIHYLEHC
EIHUDEHZENE
HEIHYLENE CHLORIDE
PICHLDRODROHOHCTHANE
TRICHL OROFLUOROHE THANC
DICHL DROPIFL UOROHE T HANE
TEIRACHLOROETHYLEHE
TCIUENE
TRICHLOfrOEIHYLENE
2i4»4-TRICNLOROPHENOL
2.4-DICHLOROPHEHOL
2.4-PIMETHYLfHCNOL
PENIACHI.OROT'HEHUL
rilEMOL
ACEHAPHTHEHE
l>2>4-lfcICMLORO»CNZENE
I.2-DICMLORO»EHZENE
I.3-DICHLOROBtNZEHE
1.4-DICHLOROSEHZENE
FLUOkANniENE
NAPHTHALENE
klS(2-ETHYLHEXYL) FHIHAIATE
»UTYL DfHZYL PIITHALAIC
DI-N-»UTYl PHIHALATE
PIETHVL PHIHAIATE
DIMETHYL PHTMALAU
li2-DENZANTHRACENE
ClIRYBEME
ANTHRACENE
PULIUIANIB HOI LISTED UtRE NEVER T'EUCIEP
tri/HOI1!!*? '"*"' t'tltL'riON ll""»' <'IESB THAN (AVERAGE CONCENTRATION) I
UNITS
HO/L
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HL/L
HO/L
HO/L
HO/I
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L <
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L <
UO/L
UO/L <
UO/L
UO/L
UO/L
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L <
INFLUENT
433
127
»73
»0
*4I
1311
1010
»
33*
1*4
1**
20
111
14
1
43
1 .
77
2
20
40
1
1
N-D
• 1
170
10
3
2
N-D
4
440
N-0
100
7
3
4
N-D
N-D
N-D
1
SECONDARY
EFFLUENT
07
10
222
3
214
1143
1047
< 1
223
204
24
13
30
2
L 1
a
N-D
24
L 1
1
11
L 1
N-D
N-D
2
94
< 1
2
2
3
3
23
2
0
< 1
N-D
L 1
L t
•
•
< 1
2
3
< t
N-D
N-D
N-D
PCHI
HEM.
00
00
77
»7
77
21
•
*4
37
-
• 7
37
71
00
.
*4
-
4*
30
»4
40
.
-
-
»7
03
*0
47
-
-
3J
*4
-
92
93
77
.
04
40
74
40
31
-
-
.
-
PRIHARY
EFFLUENI
344
230
030
43
1047
1371
1014
3
277
20*
114
20
1*0
13
< 1
21
L 1
4*
2
17
11
H-P
L 1
N-0
3*
1*4
3
< 1
2
L 1
4
411
N-D
101
10
L 1
3
N-P
74
47
4
4
t
N-D
N-D
N-D
N-D
PMHARY
SLUPOE
24011
42421
72033
9292
1333
34347
4*33
»73
24*73
204*
2413*
24
1417
20
11
N-D
71
27
74
402
47
2
4
7
140
20»*
no*
N-D
N-D
N-D
N-D
132
N-D
3400
N-D
112
1*0
102
*44
3320
400
413
N-D
N-D
49
43
140
SECONDARY
SLUbOE
10347
4110
3113
11*
343
4102
2013
*1*
2343
1120
3140
14
447
2
< t
H-D
N-D
9
N-U
3
7
N-D
N-D
2
21
47
2
N-D
H-ll
N-D
N-D
14
M-D
14
_
_
_
0
4
.
t>-
|j_
ff.
(1
-------
TABLE 19
SUMMARY OF ANALYTICAL BATA
CMAITANOOOA 4-DAY STUDY
FRACTION
DASE-NEUTRALS
PESTICIDES
METALS
HON-CONV. METALS
PARAMETER
PMENAHTIIRENE
PYRENE
ALPHA-ENPOSULFAN
AlF'HA-HIC
OAMMA-tim:
ANTIHONY
ARSENIC
tERYLLlllH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
THALLIUM
ZINC
ALUMINUM
tARIUM
IORON
CALCIUM
COBALT
IRON
MAGNESIUM
MANGANESE
MOLYBDENUM
. SODIUM
TIN
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
NO/L
NO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UB/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L.
NO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
I
< 1
617
713
V47
12
»
< 1
10
224
121
4747
114
111
pa
i
21
1
«B4
7310
173
224
44
24
4247
f
323
13
3S7
47
44
3
3
SECONDARY
EFFLUENT
< 1
L 1
L 1000
L 1000
233
4
4
L 1
4
3»
10
113
44
L 1000
82
3
2
I
?4
• 59
12
319
33
23
4»4
•
I2S
L 33
332
34
< 1
< 1
L 4
PCNT
SEM.
»0
-
-
-
74
34
S3
-
37
63
11
»B
S3
-
17
3
•r
11
Bl
SB
82
" -
1*
3
88
IB
44
1
14
1 »»
93
-
PRIMARY
EFFLUENT
3
N-P
N-D
L 1000
433
7
7
< 1
»
243
84
3230
111
L 1000
135
3
SB
1
4VO
4153
143
227
41
42
3170
•
223
4
337
33
34
4
3
PRIMARY
8LUDOE
348
223
N-0
N-P
N-D
V3
247
?0
B4
3330
»147
43730
12383
33147
2317
1
8*2
L 170 L
3066?
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NUT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
BLUDOE
a
N-D
N-D
N-D
N-P
If
}1
37
1
1213
'40
342
.19
r313
!04
i
S43
:i7
:I3S3
HOT RUN
HOI RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LISTED WERE NEVER DETECTED
I.-LESS THAN (MAX. DETECTION LIMIT) I <"LESS THAN (AVERAGE CONCENTRATION)!
N-II-NOT ntircirri.
-------
FRAC 11ON
CONVLMTIONAIB
NON-CONVENTIONAL*
VOLATILE!
Ni
AC IH EXIKACT
•ASE-HEUIfcAL!
PESTICIDES
Hf IALS
TABLE 19
SUMMARY OF ANALYTICAL PATA
CHAITANOOOA 4-Mr RTUPY
ADDITIONAL SAMfie fOtHIt
PARAMETER
TOTAL SUSP. SOLID*
COU
OIL I OKCABC
TOTAL PHENOL!
TOTAL SOLIPfl
TOTAL PISI. IOLIPI
•ETTLCAktC lOLtP!
TOTAL VOLATILE *OLIPI
VOLATILE PI!!. tOLlftl
TOTAL VOL. IU8. SOLID*
AMMONIA NITROCEH
TOC
•ENZCNE
CHLOftOIEHZENE
CHLOROE THANE
CHLOROFORM
I i 2- tHANI-DICHLOROEIHTlEME
ETHYLPEHIENC
METHTLENE CHLORIHE
PICHLOROPROMOMETIIANE
CMLOftOPIBROMOHETHANE
TOLUENE
VINYL CHLORIDE
2>4i4-TRICHLOROPHENOL
2.4-PICHLORnPHCHOL
PEHIACHLOKOPIIENUL
FIIENOL
1.2. 4-TKICMLOflO»ENZENE
1.2-PICHLONOPENZENC
lr4-PICHLOROPENZENE
FLUOR ANTHEHE
HAfHIHALCHE
PIK2-ETHTLHCXVL) PHIHALATE
•PTYL PENZYL PHTHALATC
PI-N-!UTYL PHIHALATE
PI-N-OCTVL PIITHALATE
PIETHYL PIITHALATE
PHENANTHRENE
PYftENE
ENURIN ALDEHYDE
DELIA-PHC
AN1IHIINY
AKSENIC
UNIfi
HO/I
HO /I
HO/I
HO /I
UO/L
HO/L
HO/L
HL/L L
HO/L
HO/L
«o/l
HO/L
HO/L
UO/L L
UO/L L
UO/L
UO/L L
UO/L L
UO/L L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L
NO/L
NO/L
UO/L
UO/L
VACUUM FILTER
FILTMU
•1
Ml
310
1
17*
MOO
»70
1
414
27f
44
SI
I0«
i-P
N-0
N-»
9
H-P
4
2
f
240
13
2
1
H-D
24
4
N-P
I
H-P •
2
1
H-P
H-P
H-P
3
•
PIOCBIER
SUPERNATANT
7300
4344
10400
900
14*
7334
24348
300
1704
404
1010
40
400
•
29
2
H-0
1
30
2
H-P
H-0
110
»
H-P
3
N-b
MO
430
41
77
7
170
to
30
IS
23
13
27
0
1700
1300
21
220
L
L
L
L
L
L
L
L
L
TAP
WATER
1
1
NOT RUN
3
24
132
43
1
f4
21
HOT RUN
1
4
1
H-P
H-P
17
N-P
t
1
II
2
1
N-P
M-0
N-P
N-P
1
N-P
N-P
N-P
N-P
H-P
1
N-P
1
N-li
1
N-P
N-P
N-P
N-P
2
2
POLLUTANT! N01 LISTED HERE NEVER DETECTED
H^D-NOT'DETECTED' DtrECII°" LIHM»' <*IE«! THAN IAVERAOE CONCEHIRATIOHII
-------
TABLE 19
SUMMARY Of ANALYTICAL I'* IA
CHATTANDOOA LESS THAN (AVERAGE CONCENTRATION) I
-------
TABLE 20. SELECTED POLLUTANT MASS PERCENT REMOVALS
Percent Removal
',
Pollutant'
Metals
Cadmium
Chromium
Copper
Cyanide
Lead
Mercury
Nickel
Silver
Zinc
Volatiles
Benzene
1,1, 1-Trichlorethane
Chloroform
1,2-Trans-Dichloroethylene
Ethylbenzene
Methylene Chloride
Tetrachlorethylene
Toluene
Trichloroethylene
Acids
Phenol
2 , 4-Dichloropheno 1
Base/Neutrals
1 , 2 ,4-Trichlorobenzene
1 , 3-Dichlorobenzene
1,4-Dichlorobenzene
Naphthalene
Bis(2-Ethlyhexyl) Phthalate
Di-N-Butyl Phthalate
Diethyl Phthalate
Phenanthrene
Convent ional/Non-Conventional
BODS
TSS
Primary
Treatment
25
0
21
0
12
21
0
17
18
7
13
1
0
0
16
25
10
42
0
2
12
14
0
0
0
40
0
0
10
30
Secondary
2
Treatment
42
95
75
15
69
100
49
83
70
78
80
56
100
89
47
88
86
78
92
46
79
30
88
92
77
6
36
36
86
82
Overall
Treatment
56
79
80
11
69
100
49
86
75
80
82
56
100
87
55
91
87
87
91
47
82
40
88
91
57
44
0
0
88
87
1 Priority toxic pollutants listed were detected in the influent wastewater
50 percent of the time or greater (with the exception lead and cadmium which
were detected 46 percent of the time).
2 Percent removal based on mass removal in activated sludge treatment units
alone.
64
-------
30 percent (average design removal is 60 percent). The treatment process of
consequence for the metals at MBWWTP appears to be the activated sludge process.
The secondary system effectively transfered the metal masses from the liquid
phase to the waste activated sludge. Overall removals fluctuated from greater
than 80 percent for copper, silver, and mercury to 56 and 49 percent for
cadmium and nickel, respectively.
PRIORITY TOXIC POLLUTANT MASS BALANCE ANALYSES
Mass balances for the primary treatment, secondary treatment, and total
treatment processes were calculated for the toxic pollutants cadmium and lead,
and for the priority pollutants detected 50 percent of the time or greater in
the influent waste stream. Those calculations are useful in evaluating the
fate of a particular pollutant as it travels through the treatment process. A
net pollutant loss is reflective of the pollutant being biodegraded or reduced
in some other fashion. For conservative pollutants, particularly metal frac-
tions, the summation of the influent pollutant loads should equal the summation
of the effluent pollutant loads. Table 21 summarizes the mass balance results
for the 36-day combined study. When calculating the pollutant load, if the
pollutant concentration was reported less than the analytical detection limit,
the concentration, and consequently the load, were assumed to be zero.
For the primary treatment analysis, the total influent mass is the sum of
the influent waste stream, the digester decant, and vacuum filter filtrate; the
primary effluent mass is the sum of the primary effluent waste stream and the
primary sludge. The primary treatment results exhibited a net total priority
pollutant metals increase of 16 percent; a 10 percent reduction in the volatile
organic fraction; a five percent increase in the acid extractable fraction; and
a 26 percent net increase in the base/neutral extractable pollutants. Part of
the net increase in the pollutants can be attributed to the presence of certain
pollutants in the influent waste stream at very low levels (at or near their
detection limits). These pollutants tended to concentrate in the sludge
streams and were measured, therefore, in the sludge streams rather than in the
influent. An interesting fact is that the metal laden filtrate and decant
lines are insignificant in the overall mass balance scheme due to the low
volume they represent.
Results of the secondary treatment analysis (activated sludge process
followed by chlorination) show that the metals increased substantially across
the activated sludge process, while the volatiles, acids, and base/neutral
fractions were reduced considerably "(76 percent, 91 percent, and 56 percent,
respectively). The influent secondary treatment mass is equivalent to the
primary treatment effluent load; the secondary treatment effluent mass consists
of the chlorinated effluent load and the waste activated sludge load. Because
the return activated sludge line is an internal recirculation line within the
secondary treatment process, the mass associated with the return sludge is not
of consequence. Comparison of the total, secondary, and primary mass removals
for the volatile organic pollutants strongly supports the theory that volatile
toxic pollutants are stripped from the wastewater during aeration or biode-
graded .
The tremendous net increase in the secondary treatment metal loads was not
anticipated. For each metal, the substantial increase in the effluent load is
65
-------
TABLE 21. MASS BALANCE ANALYSIS FOK COMBINED 36-DAY STUDY-
I'arameler
I«
.
Cadiiiiiia
Chromium
Copper
Cyunide
lead
Mercury
Nickel
Silver
Zinc
Volatiles
Benzene
1,1,1 ,-trichloroetliane
Chloroform
1 ,2-trans-dichloroethylene
Ethyl benzene
Methylene chloride
Tetruchloroethylene
Toluene
Trfcliloroctiiylene
Ac i ds
Phenol
2,4 Dtclilorophenol
Base/Neutrals
1 ,2,4-Trichlorobenzene
1,3-Uiclilorobeu/ene
1,4-Oichlorobenzene
Naphthalene
Bis(2-elhylhexyl)phthalate
Di-n-hulyl phthalate
Dielhyl phthalate
I'henanUu eite
1-70
76.2
30.1
28.8
16.3
0.1D4
28,3
2.99
129
6.42
8.02
25.2
0.36
C.02
28.9
20.8
146
8.15
84.7
1.65
11.1
0.73
1.9
6.9
2.7
1.8
1.5
0.4
r Treatment**
Out
1.45
96.5
33.7
31.5
21.9
0.133-
32.8
3.28
141
5.99
7.11
25.1
0.44
9.63
24.4
16.1
133
5.03
8
-------
the apparent result of the increase in waste activated sludge mass. Though
calibration of the waste activated sludge pumps to test the current actual
discharge rates was attempted, several valves that isolate the sludge wet wells
were inoperable and the pump rates could not be verified. Analytical results
and flow records were thoroughly reviewed and no errors were identified.
The total treatment mass calculations are based on the influent load
without the load from the recycle lines; the effluent load is equal to the sum
of the primary sludge, waste activated sludge, and secondary effluent waste
stream loads minus the vaccum filtrate and digester decant loads. Results of
the overall treatment mass balance analysis also indicate that volatiles,
acids, and base/neutral fractions are reduced significantly while metal masses
are observed to increase. Again, erroneous WAS pump rates are suspected as
causing the discrepency in metals loads.
CORRELATION OF INFLUENT AND EFFLUENT PRIORITY TOXIC POLLUTANT CONCENTRATIONS
Changes in secondary treatment effluent concentrations as a result of
varying influent concentrations is a subject worthy of investigation. Whether
a POTW can adequately treat a pollutant on a pound per pound basis regardless
of influent pollutant mass, and if the treatment efficiencies are predictable
are questions of concern. Linear correlations between the influent and second-
ary effluent concentrations were attempted in order to answer these questions.
The changes in selected effluent priority pollutant concentrations as a
result of varying corresponding influent concentrations is examined below by
correlating the influent priority pollutant concentrations to the secondary
effluent concentrations. In addition to cadmium and lead, correlations for all
priority pollutants that occurred in over 50 percent of the combined 36-day
influent samples were determined. Table 22 presents the correlation coeffi-
cients, the slope of the best fit line, and the y-intercept determined for each
parameter. In calculating the linear correlations, the influent and effluent
concentration were assumed to equal zero if the pollutant was not detected in
the waste stream; if the pollutant was reported as less than the analytical
detection limit, the concentration was also assumed to equal zero.
The correlations were generally good with wide variations observed within
the metal, volatile, acid, and base/neutral fractions. Correlation coeffi-
cients for the metals ranged from 0.94 for cadmium to -0.008 for mercury;
nickel, mercury, copper and zinc had the smallest slopes signifying that each
incremental increase in the influent concentration above a certain value
(y-intercept) results in a correspondingly larger incremental increase in the
effluent concentration. Chromium and silver had the steepest slopes (6.2 and
3.3, respectively), indicating that each incremental increase in the effluent
concentration is the result of the influent concentration increasing by factors
of 6.2 and 3.6, respectively.
Correlation coefficients for volatile priority toxic pollutants ranged
from 0.804 for 1,1,1-trichloroethane to 0.081 for trichloroethylene. Slopes
were slightly greater than those for the metals (denoting lower effluent con-
centrations for each incremental increase in the influent concentrations).
67
-------
TABLE 22. CORRELATION OF INFLUENT AND EFFLUENT
PRIORITY TOXIC POLLUTANT CONCENTRATIONS
Parameter
Metals
Cadmium
Chromium
Silver
Lead
Nickel
Cyanide
Zinc
Copper
Mercury
Volatiles
1,1, 1-Trichloroethane
Toluene*
Benzene
Te t r achloroethy 1 ene
Chloroform
Ethy Ibenzene*
1 , 2-Trans-Dichloroethylene
Methylene Chloride
Trichloroethylene
Acids
2 , 4-Dichlorophenol
Phenol*
Base/Neutrals
Diethyl Phthalate
1 ,4-Dichlorobenzerle
Naphthalene
Phenanthrene
1 , 2 ,4-Trichlorobenzene
Di-N-Butyl Phthalate
1 , 3-Dichlorobenzene
Bis(2-Ethylhexyl) Phthalate*
Correlation
Coefficient
0.943
0.913
0.596
0.524
0.396
0.080
0.163
0.041
-0.008
0.804
0.730
0.597
0.535
0 ..484
0 . 340
0.322
0.22
0.081
0.624
0.480
0.779
0.654
0.634
0.472
0.383
0.228
0.114
0.020
Slope
of Best
Fit Line
1.3
6.2
3.3
1.2
0.62
1.4
0.64
0.07
-0.04
3.0
8.6
2.0
5.2
1.4
1.5
0.36
0.65
0.40
1.1
3.1
0.58
2.2
3.3
1.8
1.6
0.7
0.1
0.1
Intercept
1.7
-84
6.2
37
51
753
295
85
314
4.4
78
10
19
23
16
2.0"
56
22
2.0
190
1.7
3.4
13
1.0
20
4.1
2.1
13
Outlier values are not included in correlation.
68
-------
Figure 4 graphically displays the linear correlation determination for benzene.
This analysis suggests that, at an influent concentration of 10 Vg/& or less,
benzene would not be detected in the secondary effluent waste stream; for each
subsequent increase in the influent waste stream of two ug/£, an increase of
one vg/£ would be expected in the effluent. Although the correlation coeffi-
cient of 0.597 does not indicate an unquestionable statistical relationship,
the analysis does yield an empirical correlation that describes the pollutant
tendency or expected pollutant behavior.
The acid compounds 2,4-dichlorophenol and phenol demonstrated moderate
correlations (r=0.624 and 0.480, respectively), and slopes greater than one.
This indicates that increases in the influent concentration should result in an
increase, to a lesser extent, in the effluent concentration. The base/neutral
compounds were detected at such low concentrations (often not detected or
detected at or near their detection limit) that no implied conclusions can be
drawn.
As may be ascertained from the above, the correlations determined should
only be interpreted as pollutant trends rather than definite pollutant patterns
as a result of secondary treatment.
CORRELATION OF EFFLUENT PRIORITY TOXIC POLLUTANT CONCENTRATIONS TO CONVENTIONAL
PARAMETERS
An attempt to identify linear regression correlations between secondary
effluent toxic pollutant concentrations and secondary effluent BOD5 and TSS
concentrations was pursued. The basis for this exercise is the theory that
removal" efficiencies sufficient to reduce BOD5 or suspended solids will also
reduce priority pollutants in the secondary effluent waste stream to similar
levels.
Nineteen priority toxic pollutants were detected in the secondary effluent
waste stream 50 percent or more of the time during the combined 36-day
study. Regression analysis between those pollutants and selected conventional
pollutants (BOD5_ and TSS) were poor overall. Table 23 presents the calculated
correlations.
Of the 19 priority toxic pollutants, silver and 1,2,4-trichlorobenzene
recorded the highest correlations to total suspended solids (correlation
coefficients of 0.69 and 0.61, respectively). Silver also demonstrated the
best correlation to biochemical oxygen demand (correlation coefficient of
0.50). Results of this analysis indicated that secondary effluent BOD5_ and TSS
concentrations apparantly do not have anything to do with the level of toxic
pollutants.
EFFECTS OF COMBINED SEWER FLOWS DURING WET WEATHER PERIODS
Approximately seven percent of the Chattanooga collection system consists
of combined sewers constructed prior to 1950. Chattanooga's older. Central
Business District is the center of the combined sewer catchment area. Land use
in the Central Business District is relatively high density single-family and
multi-family residential areas combined with high .rise commercial development.
The industrial sector of the city is not served by combined sewers.
69
-------
601-
55
50
45
C 40
tn
ui
u
z
UI
35
30
25
20
15
= 0.597
y=2.0x + 10
SLOPE = 2.0
• e
5 10 15 20 25 30 35 40 45
SECONDARY EFFLUENT CONCENTRATIONS (ji9/')
OBSERVED INFLUENT VERSUS SECONDARY
EFFLUENT CONCENTRATIONS FOR BENZENE
50
70
-------
23. COKKKI.ATION OF SECONDARY EFFLUENT PRIORITY POI.UITANT
CONCENTRATIONS TO SECONDARY EFFLUENT BODS AND TSS CONCENTRATIONS
_ Biotl^cmltal Oxygen Demand
Solids
Parameter
Metals
Chromium
Copper
Silver
Zinc
Cyanide
Nickel
Volat iles
Benzene
Hetliylene Chloride'*'
Telrachloroelhylene
Chloroform
Toluene
Trichloroelliylene
Ethylhmizenc
1 ,1 , 1-TricIiloroeUmne
Acids
Phenol
Base/Neut t» I s
1 ,3-Dirlilorol>t>n;sene
2,4-Dldilnro|ihenol
Diclhyl I'll thai ale
Correlation
Coefficient
0.01
-0. 10
0.50
0.10
-0.01
0.12
0.38
0.05
0.21
0.27
0.32
0.10
0.29
0.13
0.04
-0.03
-0.05
0.)2
0.0'J
Slope
0.01
-0.17
34
0.10
-0.01
0.16
2.1
0.03
0.46
0.35
0.05
0.19
1.2
0.17
0.02
-0.31
-0.88
1.3
0.45
Intercept
45
48
1.4
35
45
36
30
36
35
25
35
37
31
37
44
46
46
41
42
Correlat ion
Coef (icieut
0.02
-0.01
0.69
0.32
0.01
0.06
0.14
-0.13
0.17
-0.02
0.11
0.12
-0.03
0.01
0.05
0.61
-0.06
0.04
0.21
Slope
0.01
-0.06
15
0.15
0.01
0.04
0.84
-0.09
0.4Q
0.03
0.02
0.25
-0. 14
0.01
0.01
1.3
-0.5
0.20
0.48
InlrrcrjH
34
35
13
19
34
32
31
39
32
35
33
33
35
34
34
26
35
34
32
* Outlier vnluca are not inrliulcil in correlation
-------
Twenty diversion structures presently exist within the combined sewer
collection network, in addition to a major overflow on the trunk interceptor
and a bypass at the POTtf. During periods of rain, excess flows are discharged
untreated to the receiving streams through the regulators or at the POTtf
bypass. Rainfall was recorded during 15 of the 36 sampling periods for this
study with precipitation values ranging from trace levels on six occassions to
1.94 inches on February 10, 1981. Four of these events were over 0.25 inches
(1.94, 0.93, 0.44, and 0.96) resulting in significant increases in flow and in
certain heavy metal influent loads. Table 24 presents the influent priority
toxic pollutant metal loads for: 1) three of the four storm events (the fourth
event was not evaluated due to surcharge conditions at the influent sample
location); 2) the average load for the three storm events; and 3) the average
dry weather period influent load. The influent samples represent combined
sewer flows prior to the waste stream being pumped either to the POTW or
bypassed directly to the Tennessee River. Grab samples were collected every
hour and were manually composited over 24-hour periods. No attempt was made to
flow-proportion the composite samples during the duration of the storm event
since no accurate flow values could be obtained. The influent loadings do not
Include the pounds of pollutants discharged at any of the overflows except at
the POTtf bypass. Therefore, it should be understood that the loadings listed
represent the pollutant trend due to combined sewer flows not the total pounds
of toxic pollutants discharged per storm event to the receiving water.
Although variability in the influent loadings exist, amounts of heavy
metals resulting from combined sewer flows are obviously significant. Lead
showed the most notable increase during wet weather periods, increasing by an
average factor of 12.3 during the three storm events. Zinc, mercury, and
copper mass loads increased on the average by factors of 3.09, 2.42, and 2.08,
respectively, during wet weather. Lead compounds, used as anti-knock additives
in gasoline, are released into the atmosphere in automobiles exhaust fumes.
These compounds and, to a lesser extent, the lead compounds produced by burning
coal may precipitate to the land surface or be washed from the air by rain and
enter the sewer system as runoff during storm events. Zinc has been identified
in motor oil, transmission fluid, rubber tires, and concrete; copper is found
in antifreeze, rubber tires, and brake linings. The mercury concentrations
recorded were at such low concentrations that the results should be viewed
cautiously. Polynuclear aromatic hydrocarbons (PNAs), pyrolysis products
formed during combustion or -heating of fossil fuels, were anticipated to be
present in combined sewer flow as a result of entering the collection system as
runoff. However, PNAs with the exception of phenanthrene and naphthalene,
waich were detected predominately during dry weather, were not detected during
wet weather periods.
Lead, zinc, and copper accounted for 54 percent of the total dry weather
metal loading, and over 80 percent of the total wet weather metal loading.
Figure 5 graphically displays the daily wastewater flow, copper mass loading,
and lead mass loading. The potential effects of wet weather flow are clearly
apparent from this analysis.
Correlating the quantitative results of this study to other catchment
areas would be difficult since the results are dependent on a number of factors
including:
72
-------
TABLE 24. INFLUENT POTW METAL LOADS DURING STORM EVENTS
w
I'ui alhi'lci
Antimony
Arsen it-
Beryl 1 him
Cadmium
Chromium
Copper
l.e««l
Mf-ri-itry
Nickel
Selenium
Silver
Zinc
Average Dally
Ory Weather
Loud
1.26
1.16
0.37
1.57
96.54
28.48
4.68
0.11
27.80
Nl)
2. 18
119.32
1NFLI1EN1
February 10
(1.94 inches)
Nl)
NO
Nl)
ND
239.08
93.92
82.82
0.43
ND
ND
5.12
708,69
r LOADS ( POUNDS /D/
February 16
(0.93 inches)
ND
ND
ND
1.87
52.43
35.57
34.45
0.37
21.72
4.49
3.74
213.45
fv)
Kehruury 17
(0.44 inches)
ND
Ml)
ND
3.18
35.65
48.38
55.38
ND
ND
ND
2.55
184.61
Average Daily
Wet Weather
Load
ND
NO
ND
1.68
109.05
59.29
57.55
0.27
7.24
1.50
3.80
368.92
Ratio of
Wet Weather
lo Dry Weather
Averages
-
-
-
1.07
1.13
2.08
12.30
2.42
0.26
-
1.74
3.09
NO - Not Detected
-------
100
• FLOW
* COPPER LOADING
a LEAD LOADING
BYPASS PUMPS NOT
OPERATIONAL DURING
STORM EVENT-
22 2) 24 2S 26 27 28
100
90
80
70
60
2
50
0
o
40
-------
o antecedent dry weather conditions;
o volume, intensity, and duration of rainfall;
o catchment area land use;
o industrial activities in the area;
o size, slope, and structural condition of the collection system;
o bypass and/or regulator arrangement;
o street cleaning practices;
o topography of the drainage area;
o erosion parameters; and
o traffic volume.
The increase in the influent metal toxic pollutant load during storm
events warrants further evaluation of the quantity, source, and impact of
priority pollutant loads in combined sewers and in combined sewer overflows.
QUALITY ASSURANCE/QUALITY CONTROL RESULTS1
Prior to detailing the results of the QA/QC program during the 30-day
study, it is important to briefly discuss the objectives and the limitations of
such a program. During the 30-day study QA/QC samples were collected and
analyzed to measure the precision and accuracy of the data and blank water
samples were analyzed to identify any sampling or analytical contamination.
As previously mentioned, blank water (ultrapure deionized water) was
pumped through all automatic samplers and associated tubing throughout the
30-day period and was analyzed for priority pollutant acid, base/neutral, and
pesticide parameter. In addition, ultrapure deionized water was poured into
VOA sample bottles, exposed to the environment at the treatment plant and
hermetically sealed. These type of samples were analyzed to identify field.and
analytical contamination such as from methylene chloride (a solvent used
extensively both during field sampling and laboratory analysis) or from phtha-
late ethers (which may be associated with the sample tubing). The analysis of
blank water samples is critical, especially when the purge-trap analytical
technique (which is susceptible to contamination by residues from concentrated
samples or vapors in the laboratory) is employed.
Sporadic occurrences of methylene chloride were identified in several of
the VOA blank water samples. Thus in reviewing the methylene chloride results,
it should be kept in mind that methylene chloride results that deviate signifi-
cantly from the mean may in fact be the result of field and/or laboratory
contamination. No other pollutants were identified repeatedly or in high
concentration in the blank water samples.
The precision of the analytical results can be expressed by the standard
deviation of the analytical results of multiple duplicate or spiked samples.
The precision of the analytical results refers to the ability to reproduce the
same results, regardless of whether the results are true values or the result
of systematic analytical errors. In summary, the lower the standard deviation
the higher the analytical precision.
Based on a report prepared by Joan Fisk, formerly of the EGD Office of
Analytical Support.
75
-------
Accuracy, or validity, can be defined for a given sample matrix by measur-
ing the percent recovery of known concentrations of priority pollutants and
surrogate compounds that are spiked into both wastewater and blank water sam-
ples. Wastewater spike data are referred to as matrix spike results in this
study; blank water spike data are referred to as methods spike results.
For the purpose of this study, surrogate compounds are compounds that
behave in the same manner as the compounds they represent, but are unlikely to
occur in the environment. All deuterated priority pollutants (stable isotopes)
were used as surrogates in this study, providing good assurance of representa-
tive behavior. Surrogate compounds were added to all samples while priority
polllutants were added to only a limited number of specified samples.
Percent recovery and precision data should not be used carelessly. They
should only be applied to samples analyzed concurrently with the QA/QC samples.
Additionally, the surrogate compound percent recoveries only indicate how good
the analytical methods was for the class of compounds that the surrogate
represents.
A summary of the QA/QC results for this study is presented below. Appendix B
contains the spike percent recoveries; and the values that are considered
outliers because their percent recovery exceeded the mean percent recovery of
the spiked samples by more than two standard deviation. Outliers are data
points that statistically are not in the same sample data population as the
other data points. They are not necessarily incorrect, however, and should be
viewed in that manner.
WASTEWATER SAMPLES
The overall quality of the purgeable data is good with an average mean
recovery of 89.5 ± 16.8 percent. The only compounds found consistently in high
concentrations are benzene, chloroform, toluene, ethylbenzene, tetrachloroethy-
lene, and trichloroethylene. The first three compounds have mean recoveries of
90 percent or greater. The last three compounds have mean recoveries of 74.8 ±
22 percent, 68.4 ± 30.5 percent and 77.8 ± 16 percent, respectively, indicating
that the concentrations found for those compounds in the samples should be
considered minimum values and under certain circumstances may be adjusted for
recoveries. The high concentration of vinyl chloride in the influent sample on
March 6, 1981, is likely an artifact, since this compound is highly volatile
and did not recur throughout the study. The methylene chloride concentrations,
in most cases, are probably an artifact of contamination due to widespread
laboratory use. Overall the "ND" values should be considered valid since the
wastewater spike sample recovery data indicate that the method is suitable for
the sample matrix.
The mean percent recovery for the base/neutral priority pollutant matrix
spikes of 79 ± 18.5 is very good. Naphthalene is the only recurring base/
neutral to occur at a signifiant concentration. The mean percent recovery for
76
-------
napthalene was 85.2 ± 19.1 percent indicating the concentrations detected
should be considered valid. The surrogate matrix spikes on the other hand did
not show recoveries nearly as high as the priority pollutants - an enigma since
all the base/neutral surrogates were labeled analogs of priority pollutants in
the spike and should have behaved similarly.
Since the overall percent recoveries are above 50 percent (1,3-dichloro-
benzene at 40.8 ± 22.5 percent and hexachloroethane at 46.8 ± 24.1 percent
being the exceptions), "ND" values may be considered quite reliable, (i.e., the
method is suitable for the matrix). Precision for the base/neutrals was quite
acceptable though better for the priority pollutants than for the surrogates.
Expectedly, the acid fraction displayed the poorest percent recoveries for
both priority pollutant and surrogate matrix spikes. Phenol in high concentra-
tions was a commonly occurring acid pollutant in these POTW samples; it had a
mean percent recovery of 27.1 ± 14.2. The lower recovery for phenol indicates
that phenol at low concentrations may have been overlooked.
One explanation of the poor recoveries, particularly of phenol and 2,4-di-
methyl phenol, may be the tendency of these compounds to "cross over" into the
base/neutral fraction - a phenomenon seen frequently with these compounds, and
especially when extracted using continuous liquid-liquid extraction instead of
separatory funnel extraction.
The values for phenol reported should be considered minimum values.
Precision is poor for phenol as it is, in fact, for all of the acids. This is
reflected by the high standard deviation in relation to the percent recovery.
The pesticides QA/QC data are quite good lending validity to "ND" values.
For the metals analyzed by atomic adsorption spectrometry (selenium,
thallium, silver, arsenic, antimony and mercury), only silver was found consis-
tently above the detection limit. Values for selenium, thallium, arsenic,
antimony, and mercury were not reported above the instrument limit of detection.
The remaining metals were analyzed by plasma emission spectrometry. Of
these metals, boron data consistently portray poor precision primarily because
the detection level is high and the determined concentrations were close to the
detection limit. Recovery for boron is also poor due to the volatility of
boron. Consequently, the boron data should be used only as a present or absent
type analyte and should be considered to be minimal values.
Percent recoveries for all of the other metals are good - generally above
95 percent, except for tin. Since tin was never found above the sample detec-
tion limit, which is approximately 30 vg/fc, using the worst sample recovery
data of about 52 percent, we can assume that at most, less than 60 vg/fc of tin
are present.
Overall, the QA data for the metals analyses for the 30-day study indicate
that the numbers may be considered to present an accurate picture of those
analytes found (other than the two cited elements).
77
-------
SLUDGE SAMPLES
The percent recoveries for the volatile pollutants in the sludge sample
are very good except for toluene (59.3 ± 40.4) and tetrachloroethane (156.3 ±
29.3 - only 4 data points). The overall precision for matrix spiking is also
good with an average standard deviation of 15.5 for priority pollutants and 8.3
for surrogates. The priority pollutant and surrogate spikes both exhibit good
recovery results. The method spikes are not as satisfactory with a mean
percent recovery of 106.8 ± 43.7. Compounds occurring in significant concentra-
tions in the samples are toluene, 1,1,2-trichloroethane, 1,1,2-trichloroethy-
lene, tetrachlorlethylene, and ethyl benzene. The toluene results reported
should be considered a minimum value because of the low percent recoveries.
The other four compound concentrations should be considered reliable. "ND"
values should be considered as depicting compound presence below 10 ug/fc unless
otherwise stated.
Considering the complex matrix presented by sludge samples, the mean
average percent recovery for the base/neutral priority pollutants of 45 ± 23.4
is not bad. The majority of the compounds that were detected in the samples
have recoveries of greater than 50 percent with the exception of bis(2-ethyl-
•hexyl) phthalate (36:9 ± 22:8), butylUenzyl phthalate (22.4 ± 5.2), benzo(a)-
anthracene (15.5.± 5.0), Benzo(k)fluoranthene (35.0), and acenaphthene (44.7 ±
19.2), which appeared only once as a sample analyte. Other compounds commonly
occurring in high concentrations are 1,2,4-trichlorobenzene, benzo(a)pyrene,
chrysene, anthracene, and fluorene. The base/neutral concentrations can be
considered as minimum values. "ND" results are not as valid for the sludge
sample as they are for the wastewater samples because of both lower spiked
sample recoveries and corresponding higher limits of detection for the base/
neutral compounds in the sludge sample.
The percent recoveries for the acids are all greater than 40 percent
except for 2,4-dimethyl phenol. These recoveries approximate the recoveries
for the acid fraction in the wastewater samples. Phenol was the only acid to
be detected at high frequency and high concentrations exhibiting a mean percent
recovery of 42 ± 17.5. The reported concentrations can be considered to be
minimums. Because of the lower recoveries and higher limits of detection, "ND"
data again may be considered less reliable than for the "ND" data for wastewater
.samples.
The sludge metals appeared very erratic as far as percent recoveries are
concerned, varying from 6.0 ± 12.7 percent for selenium matrix spikes and 4.0 ±
8.9 for selenium methods spikes to 90 percent or better for zinc, beryllium,
chromium, copper, lead, nickel, and silver. All the priority pollutant elements
except selenium and thallium were detected in these samples and for most
elements, except selenium, antimony, and thallium (all determined to be below
the detection limit in most samples), data can be considered good because of
high percent recoveries. Arsenic has a very high standard deviation showing
wide variability of percent recovery. Overall, the data for the elements found
in concentrations greater than 50 ug/£ are supported by good percent recoveries.
78
-------
APPENDIX A. ASBESTOS RESULTS*
Location
Total Fibers - Chrysotile Fibers - Total Fibers - Chrysotile Fibers -
All Sizes All Sizes Restricted Sizes Restricted Sizes
(million fibers per liter) (million fibers per liter) (million fibers per liter) (million fibers per liter?
Data
1 n t e ifire ta t ion
Top Water 0
Primary Effluent 375
Influent to POTW 1100
Treated Effluent
75
Shows no indication of chry-
sotile fibers in the sample.
Cannot be Interpreted because
of the limited number of
Chrysotile fibers counted.
Shows no indication of chryso-
tile asbestos in the waste-
stream.
Shows no indication of chryso-
tile asbestos in the waste-
stream.
* Based on grab samples taken on 25 February 1981.
-------
TABLE B-l. PERCENT RECOVERIES - WASTEWATER PURGEABLE POLLUTANTS
Priority Pollutant
Matrix Spikes
[meantg, (No. of data points)]
Method Spike
Tetrachloroethylene
Toluene
1 , 1 ,2-trichloroethane
Tetrachloroe thane
Benzene
Dibromochlorome thane
cis-l,3-Dichloropropylene
Trichloroethylene
1 ,2-Dichloropropane
Trans- 1 , 3-Dichloropropylene
Bromodichlo rome thane
1,1, 1-Trichloroethane
Carbon tetrachloride
Chloroform
1 , 2-Dichloroethane
1 , 1-Dichloroethane
Trans -1,2-Dichloroethylene
Trichlorofluorome thane
Ethyl benzene
Chlorobenzene
Mean ± a
Surrogates
68.4 ± 30.5 (8)
89.5 ± 13.5 (6)
93.6 ± 14.6 (8)
93.3 ± 30.6 (8)
92.5 ± 17.7 (8)
83.6 ± 10.8 (8)
90.0 ± 17.3 (4)
77.8 ± 14.1 (8)
90.4 ± 13.8 (8)
89.0 ± 27.8 (8)
90.4 ± 15.4 (8)
97.4 ± 23.8 (8)
78.4 ± 22.9 (8)
106.0 ± 28.8 (8)
95.0 ± 22.5 (8)
97.8 ± 17.8 (8)
87.1 ± 17.8 (8)
94.8 ± 28.5 (8)
74.8 ± 22.0 (8)
85.6 ± 17.3 (8)
89.5 ± 16.8 (124)
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
d,l,2-Dichloroethane
dgToluene
d. JEthyl Benzene
Mean ± a
81,0 ± 12.8 (105)
115.4 ± 9.6 (106)
102.0 ± 16.3 (113)
102,1 ± 16.3 (113)
a = standard deviation
B-l
-------
TABLE B-2. PERCENT RECOVERIES - WASTEWATER BASE/NEUTRAL POLLUTANTS
Priority Pollutant
Matrix Spikes
[meaula,(No.of data pts)]
Method Spikes
[mean±a, (No.of data pts)]
1 ,2-Dichlorobenzene
1 ,3-Dichlorobenzene
Hexachloroethane
Bis (2-chloroisopropyl)ether
n-Nitroso-di-n-propylamine
Ni t r obenzene
Isophorone
Hexa chl o robuta d iene
1,2, 4-Trichlorobenzene
Bis (2-chloroethyl) ether
Naphthalene
Bis (2-chloroethoxy)me thane
2-Chloronaphthalene
Anenaphylene
Acenaphthen
Dimethyl phthalate
2 , 6-Dinitrotoluene
Fluorene
2 , 4- dinitro toluene
Diethyl phthalate
1,2-Diphenyl hydrazine
n-Nitroso-di-phenylamine
Hexachlorobenzene
4-Bromophenyl ether
Phenanthrene/ Anthra cene
Di-n-butyl phthalate
Fluroanthene
Pyrene
Butyl benzyl phthalate
Benzo (a) anthracene/ chrysene
Di-n-octyl phthalate
Dibenzo(ath)anthracene
Benzo (g,h,i)perylene
Bis(2-ethyl-hexyl) phthalate
Indeno(l ,2 ,3-cd)pyrene
53.0 ± 17.9 (5)
40.8 ± 22.5 (5)
46.8 ± 24.1 (5)
62.8 ± 26.1 (5)
92.3 ± 47.4 (4)
85.6 ± 37.0 (5)
76.0 ± 31.1 (5)
58.4 ± 22.3 (5)
62.2 ± 26.3 (5)
67.2 ± 30.2 (5)
85.2 ± 19.1 (5)
91.2 ± 34.8 (5)
85.0 ± 19.4 (5)
84,8 ± 20.2 (5)
76.2 ±17.0 (5)
99.3 ± 72.0 (5)
81.8 ± 16.3 (4)
87.0 ± 20.4 (5)
77.5 ± 8.5 (4)
69.4 ± 31.9 (5)
88.8 ± 24.0 (5)
104.0 ± 21.4 (8)
80.2 ± 13.4 (5)
86.0 ± 14.1 (5)
73.6 ± 25.6 (5)
97.0 ± 33.8 (5)
93.4 ± 22.2 (5)
88.6 ± 14.0 (5)
92.2 ± 61.6 (5)
76.6 ± 13.1 (5)
80.6 ± 26.4 (5)
79.5 ± 16.3 (2)
72.0 ± 17.0 (2)
85.8 ± 16.2 (5)
84.0 (2)
35.2 ± 30.2 (6)
32.0 ± 28.3 (6)
46.0 ± 38.6 (3)
50.3 ± 34.0 (9)
78.3 ± 31.1 (4)
68.5 ± 42.8 (6)
73.3 ± 49.2 (6)
45.4 ± 34.5 (5)
49.3 ± 28.4 (6)
44.7 ± 36.5 (6)
69.3 ± 34.9 (6)
76.2 ± 42.6 (6)
87.7 ± 37.5 (6)
85.5 ± 48.2 (6)
92.8 ± 42.6 (6)
68.5 ± 27.1 (6)
75.6 ± 35.0 (5)
97.2 ± 41.2 (6)
54.0 ± 43.5 (5)
72.2 ± 30.9 (6)
102.7 ± 42.4 (6)
114.3 ± 36.5 (6)
90.3 ± 44.0 (6)
97.5 ± 44.5 (6)
107.7 ± 40.6 (6)
38.3 ± ±7.6 (6)
114.5 ± 51.7 (6)
111.5 ± 41.9 (6)
81.0 ± 33.3 (6)
117.3 ± 29.9 (6)
118.5 ± 55.8 (6)
107.5 ± 54.5 (6)
84.0 ± 18.3 (3)
75.0 ± 26.0 (3)
98.7 ± 11.6 (3)
Mean ± a
79.0 ± 18.5 (139)
76.9 ± 26.7 (162)
Surrogates
d-Nitrobenzene
dftNaphthalene
d.^Chrysene
drrFluorene
a = standard deviation
52.0 ± 19.6 (75)
61.1 ± 25.9 (102)
60.9 ± 35.0 (90)
59.2 ± 24.2 (92)
B-2
-------
TABLE B-3. PERCENT RECOVERIES - WASTEWATER ACID POLLUTANTS
Priority Pollutant
Matrix Spikes
[meantq,(No.of data pts)]
d,-Phenol
d^2-Nitrophenol
Mean ± o
33.7 ± 16.4 (112)
45.9 ± 19.6 (105)
39.6 ± 19.0 (217)
Method Spikes
,(No.of data pts)]
2-Nitrophenol
2-Chlorophenol
Pheaol
2 , 4-Dimethylphenol
2 , 4 , 6-Trichlorophenol
2 , 4-Dichlorophenol
p-Chloro-ro-cresol
2 , 4-Dinitrophenol
4 ,6-Dinitro-o-cresol
Pentachlorophenol
4-Nitrophenol
Mean ± a
Surrogates
49.8 ± 22.7 (8)
42.0 ± 20.3 (8)
27.1 ± 14.2 (8)
41.5 ± 26.6 (8)
54.6 ± 26.7 (8)
54.8 ± 22.9 (8)
56.3 ± 17.1 (8)
104.5 ± 94.6 (8)
78.3 ± 70.1 (8)
73.1 ± 57.6 (8)
34.0 ± 14.0 (4)
45.0 ± 23.9 (69)
56.4 ± 22.7 (8)
40.4 ± 21.4 (8)
33.8 ± 24.8 (8)
46.9 ± 23.3 (8)
62.8 ± 24.5 (8)
58.1 ± 24.4 (8)
66.0 ± 23.8 (8)
87.0 ± 43.3 (4)
89.0 ± 16.0 (4)
82.7 ± 30.7 (7)
62.0 ± 26.6 (4)
59.3 ± 29.3 (75)
B-3
-------
TABLE B-4. PERCENT RECOVERIES - WASTEWATER PESTICIDE POLLUTANTS
Matrix Spikes Method Spikes
Priority Pollutant [mean±a, (No.of data pts)] [mean±q, (No.of data pts)]
Gamma BHC
Aldrin
Heptachlor
Heptachlor epoxide
Endrin
Dieldrin
4,4'-DDD
4, 4' -DDT
72.9 ± 17.9 (8)
80.3 ± 29.0 (8)
75.8 ± 25.5 (8)
80.0 ± 22.7 (8)
88.9 ± 43.1 (8)
81.5 ± 28.5 (8)
72.0 ± 21.2 (8)
62.8 ±28.0 (8)
67.5 ± 18.2 (8)
89.3 ± 15.6 (8)
82.3 ± 17.6 (8)
90.9 ± 22.2 (8)
87.1 ± 26.6 (8)
89.6 ± 17.9 (8)
80.1 ± 24.9 (8)
82.9 ± 33.0 (8)
Mean ± a = standard deviation
B-4
-------
TABLE B-5. WASTEWATER OUTLIERS BASED ON SURROGATE RECOVERIES EXCEEDING
TWO STANDARD DEVIATIONS
Sample Location
Date
Percent of Data
as Outliers
Acid Fraction
D^2Nitrophenol
Influent
Treated Effluent
Digester Decant
Treated Effluent
Primary Effluent
Treated Effluent
Influent
Primary Effluent
Treated Effluent
Influent
Influent
Primary Effluent
Treated Effluent
10 February 1981
10 February 1981
12 February 1981
22 February 1981
4 March 1981
4 March 1981
5 March 1981
5 March 1981
5 March 1981
8 March 1981
9 March 1981
9 March 1981
10 March 1981
10.2
D-Phenol
Primary Effluent
Influent
Primary Effluent
Treated Effluent
Primary Effluent
Volatile Fraction
D,l,2,-Dichloroethane
Influent
Primary Effluent
Treated Effluent
Influent
Primary Effluent
Treated Effluent
1 March
5 March
5 March
5 March
11 March
1981
1981
1981
1981
1981
4.3
16 February 1981
16 February 1981
16 February 1981
24 February 1981
2 March 1981
2 March 1981
6.3
DgToluene
Influent
Influent
Primary Effluent
VF Filtrate
Tap Water
Treated Effluent
Influent
Treated Effluent
23 February 1981
24 February 1981
8 March 1981
8 March 1981
8 March 1981
9 March 1981
10 March 1981
10 March 1981
7.0
B-5
-------
Table B-5. (continued)
Sample Location
Date
Percent of Data
as Outliers
D .Ethyl Benzene
Influent
Treated Effluent
Treated Effluent
Base/Neutral Fraction
DgNaphthalene
Treated Effluent
Treated Effluent
VF Filtrate
Primary Effluent
Treated Effluent
Influent
Primary Effluent
Treated Effluent
Treated Effluent
D_-Nitrobenzene
Influent
Primary Effluent
Primary Effluent
Treated Effluent
Influent
Treated Effluent
VF Filtrate
Tap Water
Treated Effluent
Influent
•-Primary Effluent
Treated Effluent
Primary Effluent
Influent
Primary Effluent
Tap Water
Influent
Primary Effluent
Treated Effluent
Influent
Treated Effluent
Primary Effluent
24 February 1981
9 March 1981
10 March 1981
2.6
11 February 1981
12 February 1981
12 February 1981
14 February 1981
16 February 1981
20'February 1981
20 February 1981
28 February 1981
8 March 1981
10 February 1981
10 February 1981
11 February 1981
11 February 1981
12 February 1981
12 February 1981
12 February 1981
12 February 1981
14 February 1981
15 February 1981
15 February 1981
16 February 1981
19 February 1981
20 February 1981
21 February 1981
24 February 1981
25 February 1981
25 February 1981
25 February 1981
28 February 1981
28 February 1981
9 March 1981
8.9
23.5
B-6
-------
Table B-5. (continued)
Sample Location
Date
Percent of Data
as Outliers
D_nFluorene
Influent
Primary Effluent
Treated Effluent
Treated Effluent
VF Filtrate
Digester Decant
Treated Effluent
Primary Effluent
Treated Effluent
Influent
Primary Effluent
Treated Effluent
Treateds Effluent
Tap Water
Influent
Primary Effluent
Treated Effluent
Influent
Treated Effluent
Influent
Treated Effluent
DI-Chrysene
Influent
Primary Effluent
Treated Effluent
Influent
Tap Water
Primary Effluent
Treated Effluent
Treated Effluent
Treated Effluent
Primary Effluent
Treated Effluent
Influent
Primary Effluent
Treated Effluent
Tap Water
Influent
Primary Effluent
Treated Effluent
Influent
Primary Effluent
Influent
10 February 1981
10 February 1981
10 February 1981
11 February 1981
12 February 1981
12 February 1981
16 February 1981
19 February 1981
19 February 1981
20 February 1981
20 February 1981
20 February 1981
24 February 1981
24 February 1981
26 February 1981
26 February 1981
26 February 1981
27 February 1981
28 February 1981
28 February 1981
8 March 1981
10 February 1981
11 February 1981
11 February 1981
12 February 1981
12 February 1981
14 February 1981
14 February 1981
16 February 1981
18 February 1981
19 February 1981
19 February 1981
20 February 1981
20 February 1981
20 February 1981
24 February 1981
26 February 1981
26 February 1981
26 February 1981
27 February 1981
27 February 1981
28 Februray 1981
19.3
8.9
20.4
B-7
-------
TABLE B-6. PERCENT RECOVERIES - SLUDGE PURGEABLE POLLUTANTS
Matrix Spikes
Method Spikes
[mean+g,(No.of data pts)]
Benzene
Carbon tetrachloride
Chlorobenzene
Chloroform
1 ,2-Dichlo roe thane
1 , 1-Dichloroethane
Ethyl benzene
1,1, 1-Trichloroethane
1,1, 2-Trichloroethane
w J
Chloroe thane
Tetrachloroethane
Trichloroethylene
Toluene
Tetrachloroethylene
Dichlorome thane
Mean ± a
Surrogates
d,-Benzene
dg-Toluene
df-1 ,2-Dichloroethane
107.1 ± 25.8 (10)
103.5 ± 39.7 (10)
112.4 ± 8.5 (10)
101.7 ± 18.3 (10)
116.3 ± 25.8 (10)
91.3 ± 10.8 (10)
131.5 ± 93.1 (10)
108.6 ± 60.3 (10)
120.3 ± 26.9 (10)
125.9 ± 129.2 (10)
156.3 ± 29.3 (4)
95.6 ± 21.9 (8)
59.3 ± 40.4 (8)
86.0 ± 23.4 (6)
61.0 ±65.4 (3)
100.49 ± 15.5 (99)
106.7 ± 11.4 (83)
100.3 ± 15.9 (84)
107.9 ± 31.6 (84)
87.0 ± 10.3 (10)
131.0 ± 24.1 (10)
88.0 ± 20.7 (10)
114.0 ± 21.7 (10)
115.0 ± 20.3 (10)
112.0 ± 17.2 (10)
102.0 ± 12.3 (10)
125.0 ± 25.8 (10)
100.0 ± 23.8 (10)
122.4 ± 95.5 (10)
95.0 ± 5.8 (4)
108.8 ± 16.6 (8)
105.0 ± 12.0 (8)
111.7 ± 23.1 (6)
71.7 ± 37.5 (3)
106.8 ± 43.7 (125)
Mean ± a
Mean ± a = standard deviation
105.4 ± 8.3 (217)
B-8
-------
TABLE B-7. PERCENT RECOVERIES - SLUDGE PURGEABLE POLLUTANTS
Priority Pollutant
Matrix Spikes
[mean±o,(No.of data pts)]
Method Spikes
[meanta, (No.of data pts)]
Heptachlor
Acenaphthylene
Benzo (a )pyrene
Bis (2x-chloroethy 1 ) ether
Bis (2-chloroisopropyl ) ether
Bis(2-ethylhexyl) phthalate
Butyl benzyl phthalate
2 , 6-Dinitrotoluene
Fluoranthene
Hexachloroethane
1 ,4-Dichlorobenzene
Naphthalene
Phenanthrene
1,2,4-Trichlorobenzene
Acenaphthene
Pyrene
Anthracene
Fluorene
Benzo (a) anthracene
Chrysene
4,4'DDE
Benzo (K) f luoranthene
1 ,2-Dichlorobenzene
Alpha BHC
Mean ± a
Surrogates
d. --Fluorene
d -Nitrobenzene
dR-Naphthalene
d. --Chrysene
39.5 ± 30.5 (10)
51.2 ± 15.1 (10)
37.5 ± 18.9 (10)
43.6 ± 22.6 (10)
43.2 ± 21.8 (10)
36.9 ± 22.8 (4)
22.4 ± 25.2 (10)
84.2 ± 24.4 (10)
52.5 ± 15.6 (10)
25.6 ± 11.5 (10)
64.3 ± 22.7 (10)
53.9 ± 23.8 (9)
54.4 ± 9.8 (7)
65.8 ± 34.4 (9)
44.7 ± 19.2 (7)
59.1 ± 10.5 (7)
55.3 ± 2.5 (8)
55.8 ± 9.8 (5)
15.5 ± 5.0 (2)
33.5 ± 19.1 (2)
45.4 ± 36.5 (10)
35.0 ± NC (1)
108.0 ± NC (1)
54.4 ± 34.2 (10)
45.0 ± 23.4 (189)
63.5 ± 35.3 (180)
106.0 ± 27.7 (80)
109.8 ± 22.9 (78)
58.9 ± 22.0 (80)
66.4 ± 54.7 (10)
48.8 ± 14.3 (10)
57.6 ± 27.1 (10)
43.6 ± 7.9 (10)
33.8 ± 20.4 (10)
13.2 ± 17.2 (10)
10.6 ± 19-2 (10)
59.4 ± 37.7 (10)
66.4 ± 16.8 (10)
33.6 ± 15.1 (10)
78.4 ± 32.6 (10)
50.3 ± 5.9 (9)
62.1 ± 21.6 (7)
68.8 ± 26.8 (10)
57.6 ± 13.3 (7)
67.9 ± 9.1 (7)
90.0 ± 43.3 (3)
53.4 ± 17.7 (5)
61.0 ± 26.9 (2)
54.5 ± 7.8 (2)
84.0 ± 67.3 (10)
90.0 ± NC (1)
125.0 ± NC (1)
64.8 ± 49.2 (10)
50.3 ± 36.0 (180)
Mean ± a
55.0 ± 17.5 (290)
a = standard deviation
NC = not calculated
B-9
-------
TABLE B-8. PERCENT RECOVERIES - SLUDGE ACID POLLUTANTS
Matrix Spikes Method Spikes
Priority Pollutant [mean±a,(No.of data pts)] [meania,(No.of data pts)]
2,4-Dichlorophenol 44.6 ± 17.1 (10) 50.4 ± 23.1 (10)
2,4-Dimethyl phenol 15.7 ± 9.4 (10) 34.2 ± 15.4 (10)
Pentachlorophenol 48.2 ± 10.8 (10) 50.0 ± 12.2 (10)
Phenol 42.0 ± 17.5 (10) 55.2 ± 17.3 (10)
Mean ± a 36.6 ± 17.9 (39) 45.3 ± 8.8 (30)
Surrogates
d,-2-Nitrophenol 44.0 ± 23.3 (79)
d^-Nitrophenol 49.0 ± 19.3 (80)
Mean ± a 41.8 ± 16.2 (136)
a = standard deviation
B-10
-------
TABLE B-9. PERCENT RECOVERIES - SLUDGE METAL POLLUTANTS
Priority Pollutant
Matrix Spikes
[meanlq,(No.of data pts)]
Method Spikes
[mean+a^No.of data pts)]
Zinc
Antimony
Arsenic
Beryllium
Chromium
Copper
Lead
Mercury
Nickel
Selenium
Silver
Thallium
Cadmium
tX»nn -4- /Y
89
31
73
110
108
107
105
71
95
6
95
47
82
7A
.4
.0
.3
.8
.2
.6
.0
.2
.9
.0
.1
.8
.2
n
+
±
±
±
±
±
±
±
±
±
±
+
±
17.5
30.1
90.5
28.5
21.7
26.9
22.0
18.7
36.6
12.7
28.0
25.7
20.7
LI i
(10)
(10)
(10)
(10)
(10)
(10)
(10)
(10)
(10)
(10)
(10)
(10)
(10)
fT)Q}
100
27
120
50
87
94
71
94
106
4
74
43
93
67
.0
.8
.4
.6
.6
.2
.2
.6
.0
.0
.8
.4
.6
ft
±
±
±
+
+
±
±
±
±
±
±
±
—
35
17
168
39
54
8
44
22
8
8
42
26
10
^0
.0
.2
.4
.7
.3
.3
.1
.2
.2
.9
.2
.3
.6
i i
(5)
(5)
(5)
(5)
(5)
(5)
(5)
(5)
(5)
(5)
(5)
(5)
(5)
ffi^t
B-ll
-------
TABLE B-10.
SLUDGE SURROGATE RECOVERIES EXCEEDING TWO
STANDARD DEVIATIONS
Sample Location
Date
Percent of Data
as Outliers
Acid Fraction
D5 Phenol
Primary Sludge
Primary Sludge
Secondary Sludge (blank)
Secondary Sludge
Primary Sludge (spike)
Primary Sludge
Primary Sludge
D^Nitrophenol
Primary Sludge
Primary Sludge
Secondary Sludge
Primary Sludge
Secondary Sludge (blank)
Secondary Sludge
Primary Sludge
Secondary Sludge (blank)
Primary Sludge
Secondary Sludge (blank)
Base/Neutral Fraction
DRNaphthalene
Primary Sludge (spike)
Secondary Sludge
Primary Sludge
Secondary Sludge (blank)
Secondary Sludge (blank)
Primary Sludge (spike)
Primary Sludge
Primary Sludge
Secondary Sludge
D^ Nitrobenzene
Secondary Sludge (blank)
Primary Sludge
Secondary Sludge (blank
Primary Sludge
Secondary Sludge
Secondary Sludge (blank)
Secondary Sludge (blank)
Secondary Sludge
Secondary Sludge (blank)
17 February 1981
18 February 1981
19 February 1981
21 February 1981
28 February 1981
3 March 1981
5 March 1981
12 February 1981
17 February 1981
17 February 1981
18 February 1981
19 February 1981
21 February 1981
3 March 1981
3 March 1981
5 March 1981
6 March 1981
16 February 1981
16 February 1981
23 February 1981
25 February 1981
3 March 1981
4 March 1981
6 March 1981
11 March 1981
11 March 1981
13 February 1981
16 February 1981
19 February 1981
23 February 1981
25 February 1981
3 March 1981
6 March 1981
8 March 1981
9 March 1981
9.1
12.2
10.3
10.1
B-12
-------
TABLE B-10. (continued)
Sample Location
Date
Percent of Data
as Outliers
D12 NitroBenzene
Secondary Sludge (blank)
Secondary Sludge (blank)
Secondary Sludge (blank)
Secondary Sludge (blank)
Secondary Sludge (blank)
Primary Sludge
DS10 Fluorene
Primary Sludge
Secondary Sludge
Volatile Fraction
DgToluene
Primary Sludge
Primary Sludge
Primary Sludge
Primary Sludge
Secondary Sludge (spike)
D,Benzene
Primary Sludge
Primary Sludge (spike)
Primary Sludge
Secondary Sludge
Primary Sludge
Secondary Sludge
Secondary Sludge
Secondary Sludge (blank)
Secondary Sludge
Secondary Sludge (blank)
D,1,2-Dichloroethane
Primary Sludge
Secondary Sludge
Secondary Sludge (blank)
Primary Sludge
Primary Sludge
Primary Sludge
Primary Sludge
Primary Sludge (spike)
Secondary Sludge
Secondary Sludge (blank)
Primary Sludge
Secondary Sludge (blank)
Primary Sludge (spike)
Secondary Sludge
Secondary Sludge (spike)
10 February 1981
13 February 1981
22 February 1981
3 March 1981
9 March 1981
11 March 1981
23 February 1981
11 March 1981
11 February 1981
19 February 1981
20 February 1981
21 February 1981
6 March 1981
16 February 1981
16 February 1981
17 February 1981
24 February 1981
26 February 1981
26 February 1981
28 February 1981
3 March 1981
6 March 1981
6 March 1981
11 February 1981
11 February 1981
11 February 1981
12 February 1981
14 February 1981
15 February 1981
16 February 1981
16 February 1981
16 February 1981
16 February 1981
17 February 1981
19 February 1981
22 February 1981
23 February 1981
6 March 1981
7.0
2.4
5.6
10.8
15.2
B-13
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENDINO 80/09/14 0800 HOURS
FRACTION
CONVENTIONALS
PARAMETER
DOD
TOTAL SUSP,
COD
OIL I GREASE
SOLIDS
O
NON-CONVENTIOHALB TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DI8S. SOLIDS
SETTLEABLE SOLIDS
VOLATILE DIS9. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
VOLATILE!!
ACID EXTRACT
BASE-NEUTRALS
PtSTirilUS
METALS
BENZENE
CHLOROtENZENE
l.iil-TRICHLOROETHANE
t>l-DICHLOROETHANE
CHLOROFORM
I> 2-TRAMS-DICHLOROETHYLENE
ETHYLBEHZENE
HETMYLENE CHLORIDE
UICHLOROIlRDHOHETHANE
DICHLORODIFLUOROHE THANE
TETRACHLOROETHYLEHE
TOLUENE
IRICHLOROETHYLENE
2» 4t4-TRICHLOROPHENOL
2.4-DICHLOROPHENOL
2t4-DIHETHYLPHENOL
PENIACHLOROPHENOL
PHENOL
l»2i4-TRICHLOROBENZENE
1>2-DICHLOROBENZENE
I>3-DICHLORO»ENZENE
1>4-OICHLOR01ENZENE
NAPHTHALENE
BISO-ETHYLHEXYL) PHTHALATE
BUTYL MEN7YL PHTHALATE
DI-N-BUTYL PHTHALATE
DILTHVL PHTHALATE
DIMETHYL PHTHALATE
ANTHRACENE
PHENANTHRENE
UAHNA-BHC
ANTIMONY
UNITS
MO/L
HO/L
H9/L
HO/L
UO/L
HO/L
HO/L
HL/L
HO/L
MO/L
MO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
INFLUENT
360
340
JIOO
82
800
1828
1292
S
232
212
18
250
9
L 1
23
N-D
128
L 1
to
9400
N-D
N-D
93
210
2
11
3
N-D
9
220
ISO
S
N-D
2
10
4
L 1
2
3
N-D
1
3
3900
9
SECONDARY
EFFLUENT
280
2?
180
2
81
1040
932
L 1
148
12
IS
42
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
N-D
3
8
N-D
10
3
N-D
N-D
N-D
1
8
3
2
5
2
N-D
N-D
L 1000
*
PERCENT
REMOVAL
90
VI
84
98
?0
42
24
80
34
94
17
83
_
-
-
-
-
-
-
-
-
-
-
-
-
»»«
-
-
99 »
?9
98
99 1
-
99f
90
-
-
-
-
-
9V*
99t
74
31
PRIMARY
EFFLUENT
280
239
950
71
484
1534
1049
L 1
242
149
IB
220
4
N-D
7
L 1
I2S
1
2
49
N-D
N-D
43
44
4
N-D
3
N-D
N-D
130
99
4
N-D
2
8
13
2
3
17
N-D
N-D
3
N-D
4
PRIMARY
8LUDOE
38000
59714
99000
10450
823
41252
8034
1000
9893
39534
35
1700
44
28
N-D
17
20
103
707
23
9
40
87
4189
4220
N-D
N-D
N-D
N-D
N-D
N-D
N-D
240
220
970
709
N-D
N-D
N-D
N-D
N-D
N-D
N-D
IS
SECONDARY
8LUDOE
44000
4030
5400
114
290
4718
1493
970
1045
2834
18
340
N-0
N-D
N-D
N-D
8
N-D
S
N-D
N-D
N-D
50
28
N-0
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
L 1
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON 80/09/14
L-LESS THAN! 0-OftEAIER THANI T-TRACEI I OR J-INTFRFEfcENCEl U-UMCONFIRMEDI
N-D-NOT DETECTED.
-------
DAILY ANALYTICAL KE8UL1S
CHATTANOOGA
SAMPLE Mil ENDIMO BO/0*/IA OBOO HOURS
n
NJ
t-KACIION PARAMETER
MEIA18 ARSENIC
ftERYlLIUM
CA»niun
ClIkOHIUH
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
8ELEN1UN
SILVER
THALLIUM
I INC
KON-COHW. METALS ALUMINUM
MRIUM
•OROM
CALCIUM
IKON
HAONE6IUM
HANOAMESE
8DDIUH
TIN
TITANIUM
YUK1UN
UNITS
UU/L
00 /L
UO/l
UO/L
UO/L
UO/L
UO/L
NU/L L
UO/L
UO/L •
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
na/L
UO/L
na/L
UB/L
UO/L
UO/L L
INFLUENT
a
1 L
»
1»»
101
3/30
124
1000 I
106
4
14
3
3a»
»t»
u*
218
3»
2220
»
2«t
471
70
If L
3 1.
8ECONKAKY
EFFLUENT
)
1
A
10
4
130
4?
1000
?t
1
3
1
121
472
30
142
33
421
7
148
321
12
2
3
fEKCENT
REMOVAL
40
•
33
»2
•4
ts
43
-
33
29
11
67
4»
BO
02
39
19
01
22
24
32
94
a»
-
PRIMARY
EFFLUENT
•
1
•
117
•2
1700
73
L 1000
127
3
14
1
913
4*00
149
304
3»
28»0
•
240
300
4f
37
9
PRIMARY
8LU00E
940
L 24 L
300
13000
17000
42*00
13000
flOOO
4400
20
1400
L 170 L
29000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
MOT RUN
NOT RUN
BECOHOAftY
SLUPOE
20
10
33
1400
»70
1400
2*0
4000
4*0
4
4*
31
1*00
NOT RUN
NOT RUN
MOT RUN
HOI RUN
MOT RUN
MOT RUN
MOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT ON B0/0*/|4
L-ltSS THAN I d-OKEAlEK THAN* T-TRACEI 1 OR J-INTERFERENCE! U'UNCONFIRMEOI
N-I»NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTAHOOOA
SAMPLE HATE ENDINO 80/09/17 0600 HOURS
FRACTION
CONVENTIONALB
PARAMETER
IOD
TOTAL SUSP
COO
OIL I CREASE
SOL IOS
n
to
NUN-CONVENT IONALB TOTAL PHENOLS
10TAL 60LIPS
TOTAL BIBB. SOLIUS
BCTTLEABLE SOLIDS
VOLATILE PISS. SOLI OB
TOTAL VOL. BUS. SOLIDS
AHHONIA NITROOEN
TOC
VOLATILES
ACID EXTRACT
BASE-NEUTRALS
PE9IICIHEB
BENZENE
CHLOKODENZENE
Irlrl-TRICMLOROETHANE
lrl-»ICHLORO£THANE
CHLOROrORH
I»2-TRAH8-DICHLOROETHVLENE
CTIITL BENZENE
HETHTLCNE CHLORIPE
TETRACHLOROETHTLENC
TOLUENE
TR1CHLOROETHYLENE
2>4»4-TRICHLOROPHENOL
2>4-DICHLOfcOPHENOL
2r4-PINETHYLPHENOL
FEMTACHLOROPHENOL
PHENOL
I>2>4-TRICHLOROBCNZEME
I>2-PICHLOROBENZENE
1>4-DICHLOROftEHZENE
FLUORANTHEME
NAPHTHALENE
BIS<2-ETHYLHEXVL> PHTHALATE
BUTYL DEHZYL PHTNALATE
OI-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
DIMETHYL PHTHALATE
l>2-t>ENZANTHRACENE '
CHRYSENE
AHIHRACENE
PHEHAHTHREME
PYRENE
ALFIIA-FNPOSULFAH
ALPHA-PHC
UNITS
HO/I
MO/L
MO/L
MO/L
UO/L
MO/L
MO/L
NL/L
NO/L
MO/L
MO/L
MO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
NO/L
SECONDARY PERCENT PRIMARY
INFLUENT EFFLUENT REMOVAL EFFLUENT
2BO
199
880
78
390
1904
1170
4
248
118
17
190
14
L 1
39
N-P
190
4
38
72
100
230
4
N-D
2
N-D
4
390
100
11
4
N-D
37
17
8
7
8
N-D
N-D
N-D
N-D
3
N-D
1000
4400
43
31
220
3
173
1214
1143
L 1
298
19
12
40
1
L 1
2
N-D
27
L 1
1
31
3
II
L 1
2
2
10
4
43
7
1
L 1
H-P
9
9
2
1
1
1
N-D
N-P
N-P
L 1
N-P
H-P
N-P
83
84
79
94
91
19
2
83
-
84
29
48
94
-
94
-
82
79
97
97
97
93
83
_
-
-
-
B9
93
91
79
-
84
71
79
84
BB
-
-
-
-
47
-
991
991
280
294
830
40
897
1932
1294
L 1
371
129
17
290
4
L 1
14
L 1
22
2
9
27
34
190
1
N-D
2
N-P
3
300
140
19
9
N-P
110
190
N-P
4
It
N-D
N-P
N-P
N-D
2
N-D
N-P
U 92000
PRIMARY
BLUDOE
2SOOO
93191
81000
11930
1249
72184
4481
1000
2128
34170
23
2400
38
20
H-B
141
38
43
424
131
1013
701
1997
N-D
N-B
N-D
N-D
N-D
B300
N-P
H-D
220
N-D
10800
790
920
N-D
N-D
270
270
407
407
330
N-D
N-D
SECONDARY
BLUDOE
3000
32B4
S200
113
402
4844
2143
929
439
3143
U
240
2
N-D
N-D
N-D
11
N-D
4
34
17
24
2
N-
N-
N-
N-
N-
43
N-
N-
N-
N-
48
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-D
N-D
FOILUTANrfi HOt LISIED UEKC NOT DETECTED AT ANY SAMPLE POINT ON 80/09/17
L-LESS THAN) 0-ORCATER THANI T-TRACEI I OR J-INTERFERENCEI U*UHCOHF1RMEDI
N-D
-------
(lAILt ANALYTICAL KE8ULIS
CHAIIANOOOA
•AMPLE PATE ENDINO OO/Of/17 0*00 HOURS
FRACTION
HE I At B
?
NOM-CONV. HETALB
PARAMETER
ANTIMONY
ARSENIC
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
NICKEL
SELENIUM
SILVER
THALLIUM
ZINC
ALUMINUM
MR I UN
CALCIUM
IRON
MAOMMIUH
MANOANEBE
SOU I UN
TIN
TITANIUM
VAN API UN
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
WO/L
UO/L
HO/L
UO/L
UO/L
UO/L L
UO/L I
INFLUENT
42
a
»
4*9
12?
4040
• 1
ta
4
if
i
40*
4*00
192
214
41
2330
•
191
341
43
U
1
]
SECON»ARY
EFFLUENT
7
3
a
33
L 2
71
L 40
fl
2
2
t
78
f22
21
793
J3
420
7
121
347
42
L 2
L 1
L 3
PERCENT
REMOVAL
•3
40
44
fl
»•
»B
91
3
47
•f
-
• 1
BO
•2
-
20
13
13
20
13
BO
-
-
PRIMARY
EFFLUENT
19
4
•
72f
77
3140
f3
130
4
12
1
3V]
7300
140
3fl
42
2740
•
If 2
341
3f
3f
2
4
PRIMARY
BLUPOE
200
200
44 L
3000
7fOO
44200
17000
3700
L 40 L
430
L 74 L
UOOO
NOT RUN
NOT MUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
KCONBARr
•LUOOE
23
If
14
1700
400
2240
120
f9
9
140
4
2800
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
PULLUTANtS NOI LIBUb WEMC NOT PEIECTEP AT ANT SAMPLE POINT ON 80/09/17
L-LE88 THANt 0-OREAU* 1MANI T-TRACEI I OR J-1NTERFERENCEI U-UMCONFIRHCOI
N-O-MOT UEIECltll,
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
ADDITIONAL SAMPLE POINTS
SAMPLE DATE ENOIHO BO/Of/17 OBOO HOURS
FRACTION
COHVENTIONALB
o
Ul
PARAMETER
BOO
TOTAL SUSP. SOLIDS
COD
OIL t OREABE
NON-CONVENTIONALB TOTAL PHENOLS
T01AL SOLIDS
TOIAL Dtse, SOLIDS
BEITLEABLE SOLIDS
TOIAL VOLATILE SOLIDS
VOLATILE 0198. 80L1H8
TOTAL VOL. SUB, SOLIDS
AMMONIA NJMODEM
IOC
VOLATILE8 BENZENE
CIILOROBENZENE
CHLOROETIIANE
Irl-TRAHS-OICHLOROETHYLENE
ETHYLDEHZENE
METHYLENE CHLORIDE
TOLUENE
VINYL CHLORIDE
2r4~niCHLOROPHEHOL
PHENOL
lr2i4-TRICHLOR00EHZENE
IrZ-PICHLOROBENZCHE
lr4-DICHLOR08ENZENE
FLUORANTHENE
NAPHTHALENE
BIS<2-ETIIYLHEXYL> PHTHALATC
BUTYL PENZYL PHTHALATE
DI-N-BUTYL PHTHALATE
DI-N-OCTYL PHTHALATE
DfETHYL PHTHALATE
PHENANTHRENE
PYREHE
PESTICII'EB ENDRIH ALDEHYDE
DELTA-BHC
METALS ANTIMONY
ARSENIC
BbRTUIUH
CADHIUH
CHROMIUM
CUPPER
POLLUTANTS NOT LIBICD WERE NOT DETECTED AT ANY SAMPLE POINT ON BO/09/17
L-LEB3 THANI 0-OHEATER TMAHt I-TRACEI I OK JiIHTCRFEREHCEl U'UNCONFIRHEDI
N-D-NOt DETECTED.
ACID EXTRACT
BASE-NEUTRALS
UNITS
HO/L
HO/L
HO/I
HO/L
UO/L
no/L
NO/L
HL/L
NO/L
NO/L
NO/L
MO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
VACUUM FILTER
FILTRATE
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT KUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOt RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUN
HOt RUN
HOT RUN
NOT RUN
NOT RUN
HOt RUN
NOt RUN
HOT RUN
NOT RUN
NOf RUN
HOI RUN
HOT RUN
HOT RUN
DIOEBTER
SUPERNATANT
7900
4944
10400
goa
344
7324
24248
200
3704
tot
3030
40
480
S
23
2
3
38
2
110
»
3
140
430
43
77
7
170
»a
30
13
23
13
27
8
1700
1300
21
228
11
74
2300
2440
TAP
WATER
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOt RUN
NOt RUN
NOt RUN
NOt RUN
HOt RUN
NOt RUN
NOt RUN
HOt RUN
HOt RUN
HOt RUN
NOf RUN
NOt RUN
NOt RUN
HOt RUN
HOt RUN
NOt RUN
NOt RUN
HOI RUN
HOt RUN
HOt RUN
HOt RUN
HOt RUN
NOt RUN
NOf RUN
HOT RUN
NOT RUN
HOT RUN
nor RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOf RUN
HOT RUN
NOT RUH
NOt RUN
HOf RUH
-------
DAILY ANALYTICAL RESULTS
CHATIAHOOOA
AlibiIIONAL SAMPLE POINTS
•AMPLE DATE ENDINO OO/OV/17 0800 HOURS
FRACfION
HEIALB
MOM-CUNV. HE1AL8
n
PARAMETER
LEAD
hERCUHV
NICKEL
BELEN1UH
SILVER
ZINC
ALUMINUM
BARtun
•OfcON
CALCIUM
COiALT
IRON
MADHESIUM
HANOANEBE
NOLVDftENUN
•ODIUM
TIN
TIIAHIUH
WAN All IUH
YTTRIUM
UNITB
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
UO/L
UO/L
UO/L
VACUUM FILTER
FILTRATE
DIOSBTEK
SUPERNATANT
NOT HUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOI RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUM
NOT RUN
2100
29000
1040
2*
300
•300
t2900
2710
411
StJ
3*0
• 4200
•3
3780
IS«
3J»
184
80»
»3
111
TAP
UATER
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOI RUN
NOT RUN
NOT RUN
HOT RUH
NOT RUH
NOT RUN
NOT RUH
NOT RUN
POLLUTANTS NOI LIBUU UEKC NOT DEIECTE6 AT ANY SAMPLE POINT ON Oft/Ot/17
L-LE8S THAN) 0-CftEATER THANI T'TRACEI I OR J-IHTERFEREMCEI U'UMCONFIRNEDI
N-»»NOI PETECTEP.
-------
DAILY ANALYTICAL RESULTS
CHAITANOOGA
SAMPLE DATE ENDING 80/09/18 0800 HOURS
FRACTION
CONVENTIOHAL8
PAD Ann en
•Ob
TOTAL BU8P
COO
OIL I 0*1ASE
SOLIDS
n
i
HON-CONVENT IOHAtB TOTAL PHENOL8
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
8CTTLCADLC SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI88, SOLIDS
TOTAL VOL. SUS. SOLIDS
AHHONIA NITROGEN
TOC
VOLATfLES
ACID EXTRACT
•ASE-NEUIRALS
PESTICIDES
DENZENE
CHLOROtENZENE
l.lrl-TRICHLOROETHANE
Itl-DICHLOROETHANE
CHLOROFORM
t«2-TRAH8-DICHLOKOETHYLENE
ETHYLBENZEHE
HEIHYLEHE CHLORIDE
TRICHLOROFLUOROHE THANE
01CHLORO DIFLUOJtOME THANE
IETKACHLOROE THYLENE
TOLUENE
TRICHLOROETHYLENE
2r4i*-TRICHLOROPHENOL
2M-DIGHLOROPHENOL
PEHTACMLOROPHENOL
PHENOL
ACENAPHIHENE
IP2,4-TRICHLOROBENZENE
I>2-DICHLORO>ENZENE
I.3-DICHLOR08ENZENE
1t 4-PICHLOftO»ENZENE
FLUORANIHENE
NAPHTHALENE
• I8(2-ETMYLHEXYL> PHTIIALATE
•UTTL tiENZYL PHIHALATE
D|-N-»UTYL PHTNALATE
HIETHYI. PHTHALAIE
MIENANIHRENE
PYRENE
OAHHA-liHC
UNITS
HO/L
HO/L
HO/L
HO/L
00 /L
HO/L
HO/L
HL/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
00 /L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
SECONDARY PERCENT PRIHARY PR1HARY
INFLUENT EFFLUENT REHOVAL EFFLUENT SLUDOE
540
137
1300
MB
too
1*30
Il2ff
11
4M
20;
214
If
240
2?
2
140
1
110
2
•
99
N-D
N-»
91
2SOO
e
N-D
3
*
420
N-D
73
10
N-D
*
N-D
120
1*
4
9
4
4
N-D
U 12000
49
91
270
NOT RUN
I4S
I2BB
121*
L I
304
210
39
II
97
3
L 1
2
N-D
If
L 1
L 1
13
N-D .
H-i
2
ISO
L 1
3
3
7
7*
7
14
2
N-D
L 1
H-D
24
29
N-D
3
2
L 1
N-D
1400
f2
8«
7f
-
79
21
-
93
38
-
B4
12
7*
Bf
90
*f
fft
83
90
SB
76
-
-
ft
f4
88
.
-
.
B2
.
79
80
-
B3
-
SO
-
99*
40
90
79
-
BB
989
332
1100
93
to*
1442
1144
L 1
3*0
23*
23*
If
2*0
2*
2
4B
L 1
*l
2
f
4*
N-D
N-D
43
tso
«
N-D
2
•
320
N-D
170
20
N-D
f
N-D
140
4*
IB
10
7
9
N-D
U 9100
31000
42204
7fOOO
I24SO
107*
99210
7BOO
1000
31*7*
' 3147
2*123
1*
1400
88
44
N-D
129
*l
24
491
148
34
N-D
f*3
*iao
889
N-D
N-D
N-D
N-D
N-D
3800
N-D
370
320
3SO
1100
4300
N-D
N-D
N-D
N-D
420
N-D
SECONDARY
SLUDOE
4200
3333
4000
fO
402
4922
1»74
fSO
2412
1184
2*32
IS
*00
4
2
N-D
N-D
14
N-D
9
f
N-D
14
I*
178
2
N-
N-
H-
N-
N-
N-
N-
N-
N-
N-
N-
37
N-
N-
N-
N-
H-
N-D
POILUTANTS NOT LI8IEH UlfcE HOT DETECTED A1 ANY SAMPLE POINT ON 80/09/16
L-LESS THAN! O-OftFATEft THAN* T-TRACEt I Oft J-INIEKfERENCE• U'UNCONFIRNEDI
H-D-NOT
-------
DAILY ANALYTICAL RESULTS
CHAITANOOUA
SAMPLE DATE ENPINO 80/OV/IS 0100 HOURS
O
00
FRACTION PARAMETER
METALS ANTIMONY
AK8EN1C
•CRYLLIUH
CADMIUM
CHROMIUM
COf t fit
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
TIIALLIUH
ZINC
NON-CONV. HtTALS ALUMINUM
MftlUM
»ORON
CALCIUM
COBALT
IRON
HASHESIUM
NAHOANESC
SODIUM
TIN
TITANIUM
VAMAOIUM
YTTRIUM
UNITS INFLUENT
SECONDARY PERCENT
EFFLUENT REMOVAL
PRIMARY
EFFLUENT
PRIMARY
SLUDOE
SECONDARY
SLUDOE
UO/L 4
UO/L 4
UO/L L I
UO/L f
UO/L 134
UO/L 144
UO/L 1320
UO/L 144
NO/L 2000
UO/L tl
UO/L 2
UO/L 12
UO/L I
UO/L 712
UO/L 0110
UO/L 242
UO/L l»S
MO/L 44
UO/L L 30
UO/L 3230
HO/L 10
UO/L 22*
MO/L 422
UO/L 79
UO/L 70
UO/L 1
UO/L 3
4
4
L I
4
4t
140
fO
L 1000
4
2
I
II SO
14
14*
11
L 30
374
7
111
404
94
L 2
L 2
L 4
11
11
• I
fS
?9
II
90
14
?4
• 7
•4
•3
21
•V
10
92
4
21
»7
11
20
4
9
L I
10
279
f]
2790
129
L 1000
f4
2
19
I
444
9110
147
147
40
94
1140
1*7
If4
99
12
3
3
110 23
110 22
L 170 ••
49 L 14
9000 740
f700 1*0
43400 2430
*200 140
120000 L 4000
1400 7*
L 12 4
410 110
L 21 L 4
30000 2100
NOT HUN
NOT RUN
MOT RUH
NOT HUN
NOT RUN
NOT RUN
NOT RUN
NOT RUH
NOT RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
HOT RUN
NOT RUH
HOT RUN
HOT RUN
HOT RUN
NOT RUN
HOI RUN
NOT RUN
HOI RUN
NOT RUN
HOI RUH
POLLUTANTS NOT LISTED UCftE NOT PETCCTED AT ANY SAMPLE POINT OH BO/OV/I*
I-LESS THANI d'OREATER I MAN I T-If) ACE I I OR J-INTERFERENCEI U'UNCONFIRMEDI
N-D-NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
ADDITIONAL SAMPLE POINTS
SAMPLE PATE ENDINO BO/OV/IB 0800 HOURS
FRACTION
CONVENT IONALB
PARAMETER
too
TOTAL SUSP
COP
OIL t OREASE
SOL ii>a
n
NON-CONVENTIONALB TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI8S. SOLIDS
TOTAL VOL. SUB, SOLIDS
AMMONIA NITROOEN
TOC
VOLATILEB
ACID EXTRACT
BASE-NEUTRALS
METALS
TOLUENE
2>4>«-TRICHLOROPHEHOL
2>4-DICHLOROPHENOL
PENTACHLOROPHENOL
PHENOL
li2.4-TRICHLOROiEMZENE
li2~DlCHLOROBENZENE
NAPHTHALENE
•1842-ETHVLHEXYL) PHTHALATE
DI-N-iUTVL PHTHALATE
OIETHTL PHTNALATE
ANTIMONY
ARSENIC
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
NICKEL
SELENIUM
SILVER
THALLIUM
ZINC
NON-CONV. METALS ALUMINUM
BARIUM
BORON
CALCIUM
IRON
NAONE8IUH
MANOANESC
SODIUM
POLLUTANTS NOT LUTED UEftC NOT DETECTED AT ANY SAMPLE POINT ON BQ/Ot/10
L-LESS THAHI O'ORCATER THANI TMRACEI I OR J-INTERFERENCEt U-UNCONFIRHEDI
N-D-NOT DETECTED,
UNITS
MO/L
MO/L
HO/L
HO/t
UO/L
HO/L
MO/L
MO/L
HO/L
MO/L
HO/L
HO/L
UO/L
VO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
HO/L
VACUUM FILTER
FILTRATE
01
141
100
3
179
1400
970
414
27»
44
91
100
2
4
2
*
240
11
2
24
«
I
2
3
B
11
70
91
2700
149
BS
4
11
1
193
24 7O
103
144
110
21(0
J7
iai
247
DIOESTER
SUPERNATANT
NOT RUN
HOI RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUH
HOT RUH
HOT RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUH
NOT RUH
NOT RUH
NOT RUN
NOT RUH
HOT RUN
NOT RUN
NOT RUH
NOT RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUH
HOT RUN
NOT RUH
NOT RUN
HOT RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
HOT RUN
HOT RUH
NOT RUN
TAP
HATER
NOT RUH
HOT RUH
NOT RUN
NOT RUH
HOT RUH
NOT RUH
NOT RUH
HOT RUN
HOT RUH
NOT RUH
HOT RUN
NOT RUH
HOT RUH
HOT RUN
NOT RUH
HOT RUH
NOT RUN
NOT RUN
NOT RUH
HOT RUH
HOT RUH
HOT RUH
HOT RUH
HOT RUH
HOT RUH
HOT RUH
HOT RUN
NOT RUH
HOI RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUN
HOT RUH
NOT RUH
HOT RUH
HOT RUN
-------
DAILY ANALT1ICAL RESULTS
CHATTANOOOA
ADDITIONAL SAMPLE POINTS
SAMPLE HATE ENDINO B0/0»/l» OB09 HOUR!
VACUUM FILTER DIK8TEH TAf
FRACTION PAKAMEItR UNITS FILTRATE IUPERMATANT HATCH
NON-CONV. METALS TIN UO/L ffl NOT RUN NOT RUN
TITANIUM UO/L 21 NOT RUN NOT RUN
TITRIUM UO/L 4 NOT RUN NOT RUN
n
H*
o
POLLUTANTS NOT LISTED MERE NOT DETECTED AT ANT SAMPLE POINT ON 80/0»/IS
L-LESS THANI 0«OREATER THAN) T-TRACEI I OR J-INTERFERENCE I U'UNCONFIRHEDI
N-D-HOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOOA
SAMPLE BATE CNDINO 00/0»/IV OOOO HOURS
FRACTION
COMVENTIONALI
PARAMETER
• OP
TOTAL SUSP
COD
OIL I OREA6E
SOLItiS
NON-CONVEMUONALS TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DISS. SOLIdS
9CTTIEABLE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
ANNONIA NITROOEN
IOC
VOLATILES
ACID £XTRACT
•ABE-NEUTRALS
PtSIICitiEB
HEIALS
BENZENE
CHLOR01ENZENE
liI.l-TRICHLOROETHANE
It1-blCHLOROETHANE
CHLOfcOFORH
1,2-TRANB-DICHLOROETHYLENE
CTHYLBENZEME
NETHYLENE CHLORIDE
TETRACHLOkOETHYLENE
TOLUENE
TRICHLOROETHYLENE
2>4-blCHLOftOFHENOL
PEMTACHL OROPHEHOL
PHENOL
lr2t4-TRICHLOROBENZENE
1.2-D1CHLOROBENZENE
|p3-DICIILOROBENZEHE
1»4-DICHLOROBENZEME
FLUORAHTHENE
NAPHTHALENE
•IB42-ETHYLHEXYL) PHTHALATE
•UTYL BENZYL PHTHALATE
DI-H-BUTYL PHTHALATE
DIETHYL PHTHALATE
tt2-BENZAHTHRACENE
CHRY8ENE
ANTHRACENE
PHCNANTHRENE
PYRENE
(JAHMA-UHC
ANTIMONY
ARSENIC
UNITS
MO/L
HO/L
HO/L
HO/L
UO/L
HO/l
MO/L
ML/L
HO/L
MO/L
HS/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L'
UO/L
Ud/L
UO/L
UO/L
NO/L
UO/L
UO/L
INFLUENT
410
444
1100
112
IOBV
2054
IU4
12
202
21*
22
ISO
I*
L 1
8
L 1
34
1
4
SB
37
l»o
3
1
7
720
1 10
12
N-D
»
N-0
190
10
2
4
9
N-D
H-D
N-D
3
H-D
1»00
4
10
SECONDARY
EFFLUENT
to
93
210
4
210
134*
1281
L 1
28*
40
12
SB
2
N-D
2
N-0
40
L I
L 1
B
3
37
L 1
1
N-P
1
3
L 1
H-D
L 1
L 1
3
7
L 1
2
A
H-D
M-D
N-D
2
L 1
L 1000
1
4
PERCENT
REMOVAL
07
•f
79
97
• 1
34
-
»2
-
03
43
41
BB
-
79
-
-
-
03
•4
•2
01
47
_
»»»
W
•a
»2
-
Bf
-
?7
30
SO
SO
-
-
-
-
33
-
47
79
7B
PRIMARY
EFFLUENT
300
219
TOO
30
1B14
J7B8
U»3
L 1
2»0
100
20
1*0
If
L 1
19
L 1
54
2
*
43
33
330
4
1
14
*00
1*0
13
N-D
8
«-D
140
14
9
9
9
N-D
H-D
H-D
9
N-D
H-D
6
12
PRIMARY
SLUDOE
29000
30000
80000
7900
2312
43794
3043
?29
432
20217
22
1200
N-D
41
N-0
3»
44
13
290
4»
T7
*74
1B2
H-»
N-D
»IO
3tOO
N-D
100
1*0
1*0
1400
4200
420
920
H-D
120
120
3BO
980
170
N-D
V9
190
SECONDARY
SLUDOE
4400
S2f4
4400
119
34*
9940
2393
»»0
1*18
4118
14
330
2
H-D
N-D
H-D
12
N-D
*
N-D
17
f9
N-D
N-
H-
20
H-
N-
N-
N-
N-
97
21
N-
N-
N-
N-
N-
4*
44
N-D
N-D
12
21
POLLUTANTS NOT LI SUP UEDE NOT DETECTED AT ANY SAMPLE POINT ON BO/OT/19
L-LCSS THANI 0-OREAIER TltANI T-TRACEI I OR J-INTERFERENCE I U-UNCONFIRHEDI
N-D-NOT liETECKIi.
-------
**HT ANALYTICAL KE8ULTB
CHATIANDOOA
SAHPLC DATE EMDIHO BO/0*/1V 0*00 HOURS
TRACTION PARAMETER
C1
H->
NJ
METALS BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CVAHIIlE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
THALLIUM
1INC
MON-CONV. NETALS ALUHlNUit
BANIUM
DURON
CALCIUM
COBALT
IRON
HAONEBIUH
HANOAHEBC
MOLYBDENUM
SODIUM
TIN
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
NO/L
UO/L
UO/L
MU/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
1
10
24*
124
4920
144
1000
121
2
24
1
32*
13100
211
ISI
Si
87
t!20
12
24*
41
411
SO
10*
u
»
SECONDARY
EFFLUENT
L 1
7
Si
12
104
74
L 1000
ii
S
4
1
77
1110
IS
2il
13
34
i»
•
too
L 13
419
iS
1
L 2
L 4
PERCENT
REMOVAL
_
10
'•L-
»»
»8
S3
-
4i
-
01
-•
03
fl
02
-
IS
3ft
»1
11
97
13
.
-
»?
OB
Si
PRIMARY
EFFLUENT
L 1
*
147
00
3100
11*
L 1000
101
4
23
1
408
0230
144
lit
42
il
4010
»
201
L 13
411
97
31
i
i
PRIMARY
SLUDOE
L 1*0 L
L 11 L
1000
3100
44000
11000
L 10000
1200
L 2i
320
L 0 L
24000
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUM
NOT fcUM
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUM
NOT RUN
HOI RUM
HOT RUN
SECONDARY
SLUDOE
70
Ii
1400
420
1700
700
0000
130
i
liO
i
4200
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUM
NOT RUN
NOT RUN
NOT RUN
POILUIANT8 NOI UBIED UEfcE NOT DETECTED AT ANY SAMPLE POINT ON OO/OV/I*
1-lESS IMANI O'OREAIEk Til AM I T-TRACEI I OR J- INTERFERENCE I U-UHCONFIRHE0I
N-b'NUI UtUCItd.
-------
DAILY ANALYTICAL RESULTB
CHATTAHOOBA
. ADDITIONAL SAMPLE POINTS
SAMPLE DATE ENDINO 60/09/lf 0800 HOURS
FRACTION
CONVENT IONALB
PARAMETER
BOD
OIL I OREA8E
NON-CONVENTIONALS TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DI88, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOC
n
VOLATILES
•ASE-NEUTRALS
METALS
CHLOROFORN
DICHLOROBROHONETHANE
CHLORODIBROMONETHANE
TOLUENE
BIB42-ETHYLHEXYL) PHTHALATC
ANTIHONT
ARSENIC
CADNIUN
CHROMIUN
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
ZINC
NON-CONV. NETALB ALUMINUM
BARIUM
CALCIUM
COBALT
IRON
HAONEBIUH
HANOANESE
SOD I UN
TIN
VANADIUM
UNITS
HO/L
HO/L
UO/L
HO/t
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L
VACUUM FILTER
FILTRATE
NOT RUM
HOT RUM
NOT RUM
HOT RUM
HOT MUM
HOT RUM
HOT RUN
HOT RUM
NOT RUN
NOT RUM
HOT RUM
NOT RUM
NOT RUN
HOT RUN
HOT RUM
HOT RUM
MOT RUM
HOT RUN
HOT RUM
NOT RUN
HOT RUM
NOT RUN
NOT RUN
HOT RUN
HOT RUM
MOT RUN
HOT RUM
NOT RUN
NOT RUN
NOT RUM
HOT RUM
MOT RUN
NOT RUN
NOT RUN
NOT RUN
BIOESIER
SUPERNATANT
NOT RUM
MOT RUM
MOT RUH
HOT RUM
HOT RUM
MOT RUM
NOT RUM
MOT RUM
HOT RUN
NOT RUN
NOT RUM
NOT RUM
NOT RUM
NOT RUM
HOT RUN
NOT RUM
MOT RUM
MOT RUH
MOT RUN
MOT RUN
MOT RUN
NOT RUH
NOT RUM
MOT RUH
HOT RUM
HOT RUM
NOT RUH
NOT RUN
NOT RUH
HOT RUM
MOT RUM
HOT RUN
NOT RUN
NOT RUN
HOT RUN
TAP
HATER
1
S
2«
192
43
f4
21
4
)7
II
2
1
1
2
2
f
7
20
50
02
fOOO
11
2
2
It
BO
24
24
73
*»
s
s
10
3V
3
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON 80/07/lf
L-LES8 THAN! 0-OREATER THAN I T-TRACEI I OR J«INTERFERENCE I U-UHCOHFIRHEDI
M-Ii'HOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHAI1AHOUOA
SAMPLE PAIC ENDING BO/OV/20 OflOO HOURB
FRACTION
PARAHEfER
CONVCNI tONAiS »U|l
TOTAL SUSP. SOLIDS
COD
OIL I OREABC
NUN-CONveNIIONALO IOIAI PHENOLS
TOTAL SOLIDS
IOIAI PISS. SOLIDS
SEIUEAtLE SOLIDS
TOTAL VOLATILE 8011 DM
VOLATILE DISS. BOLItiB
TOTAL VOL. SUB. BOLID8
AltrtOHIA NIIROOEN
IOC
VOlATIltS
ACID EXTRACT
MAEE-NEUTRALS
PES1 ICIIlES
HL'IAIB
DCNZENE
CULORODENZENE
lilil-TRICHLOROETHANE
CHLOROFORM.
1>2-TRANS-DICHLOROETHVLENE
ETHVLDENZENE
HETHYLENf CHLORIDE
TETRACHLOROCTHVLCME
TOLUENE
TKICHLOROCTHYLENE
2.4'4-TRICHLOROPHENOI.
2.4-DICHUOROPHENOL
PEHTACHLOROPHCNOL
PHENOL
ACENAPHTHEtiE
li2>4-TRICiHORO»ENZEHE
i.2-Ii|CHLO((OI.EN2£ME
Iil-DICHLORODENZENE
li4-DICHLOKO»ENZENE
FLUOftANTHENE
HAPHIHALENE
HI8<2-EIHYUIEXrL) PHTHALATE
BUTYL DENZYL PHTHALATE
DI-N-«UTYL PHTHALAIE
DIETHYL PHTHALATE
ANTllRACtNE
PHENANIHREHE
PYRtHE
OAHHA-liHC
ANIIHONY
ARSENIC
UNITS
MO/L
MO/L
MO/L
HO/L
UO/L
HO/L
MO/L
ML/L
MO/L
HO/L
MO/L
MO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
WO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUEI
440
142
BIO
41
1*11
1004
4V2
10
270
Bl
219
21
140
11
2
10
1*
1
3>
4
170
970
31
1
2
9
4BO
N-D
92
4
2
1
N-D
44
19
2
1
10
N-D
2
N-D
SECOHDA
«T EFFLUEN
99
44
210
4
344
11*2
1010
2
222
IB4
14
14
48
1
L 1
L 1
19
L 1
2
9
1
39
L t
2
L 1
4
19
2
10
L 1
N-D
L 1
N-0
4
2
N-D
I
1
N-D
L 1
N-D
RY PERCE
T REHOV
OB
08
72
*3
71
-
-
BO
IB
•
•9
]»
44
*l
90
to
21
47
t9
17
*B
t4
97
33
SO
94
9B
.
01
79
t*l
47
-
fl
07
99 1
47
*0
-
SO
-
NT PRIMARY
AL EFFLUEN
140
1*1
420
11
1284
*B4
724
4
228
81
112
21
110
II
L 1
IB
21
3
44
3
44
480
4
3
L 1
7
430
N-D
31
2
L 1
2
N-D
21
t
1
2
11
N-0
2
N-D
PHI NARY
r BLUDOE
17000
42000
33000
9*00
2949
32484
4800
990
27180
2000
21000
32
1300
H-P
44
N-D
N-D
123
213
30
N-D
922
47
N-D
N-D
N-D
N-D
N-D
2*00
N-D
N-D
240
202
1800
4040
840
710
N-D
920
920
210
BEI
6LI
1B<
414
34<
201
943
471
211
90<
24 f
n:
2*:
13
42!
2
N-l
N-l
3
N-l
3
N-l
22
41
7
N-
N-
N-
N-
N-
N-
N-
N-
N-
H-
H-
20
H-
H-
N-
N-
N-
N-
.OHDARY
IPOE
10
U
)0
»
1
14
H
>
12
17
10
1
1
)
»
»
HO/L U 7700
UO/L
UO/L
8
12
N-D
POLLUIAHIS HOT LlbfEl' UthE HU1 DETECTED AT ANY SAflPLE POINT ON BO/OV/20
I-I ESS THAN) 0-OREAIER TIIAMf T-TRACEI I Oft J-IHTERFCREHCEI U'UHCONFIRHEDI
H-I'-NOI DETECTED.
IB
90
1000
4
10
N-U
74
200
N-D
24
24
-------
HAIL* ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE CNIiINO 80/09/30 0800 HOURS
FRACTION
HEIALS
o
NOH-CONV. METALS
PARAMETER
BERYLLIUM
CAUHIUH
CHROMIUM
COPPED
CVANIliE
LEAH
HEkCURY
NICKEL
BELCN1UH
SILVER
THALLIUM
ZINC
MLUNIHUH
»AR|UN
BORON
CALCIUH
COBALT
IRON
MAGNESIUM
MANGANESE
MOLYBDENUM
SODIUM
TIN
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
M.Q/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
L 1
10
110
129
79(0
192
L 1000
HO
3
23
1
471
79BO
190
20*
42
90
4430
a
321
30
240
4»
4«
8
9
L
L
L
L
L
L
L
SECONDARY
EFFLUENT
1
9
40
20
72
81
1000
103
2
2
2
fO
8*2
34
2I»
37
90
942
8
til
39
397
78
2
t
3
PERCENT
REMOVAL
_
SO
4»
84
99
47
-
24
33
tl
-
81
88
77
24
12
14
87
-
44
8
-
-
»4
88
40
PRIMARY
EFFLUENT
L 1
I
104
4V
4430
113
L 1000
277
3
18
2
322
3940
114
77
42
71
2920
8
234
38
242
47
18
2
4
PRIMARY
8LUDOE
310
L 42 L
4000
8VOO
3V400
14000
L 12000
1400
L 32
»40
L 8 L
2*000
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
SECONDARY
8LUDOE
74
14
720
400
2980
740
fOOO
240
4
180
37
4200
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUH
HOT RUN
NOT RUH
HOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT I IBTEIi UEkE NOT DETECTED AT ANY SAMPLE POINT OH BO/Of/20
L-LC3S THANI O'OREAICR THANI T'TRACCI I OR J-JMIERFERENCEI U-UNCONFIRMEDI
N-ri*Moi IIETECTCD.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOOA
•AMPLE DATE EHPIMO MO/09/21 OBOO HOUKB
FRACTION
CONVENTIONAL*
PARAMETER
TOTAL SUSP
COP
OIL I PREA8I
BOL1PB
O
I—•
cn
NON~CONVEM1IONAL8 TOTAL PHENOLS
TOTAL SOL 108
TOTAL DIBS. BOLIDB
SETUtAftlE 60LIB9
TOTAL VOLATILE BOLIDS
VOLATILE DISB. SOLIDS
IOTAL VOL. bU8. BOLIOB
AMMONIA NITROGEN
TOC
VOLATILEB
ACID EXTRACT
HABE-NEUTKAL0
PESIICIPEB
METALS
•ENIENE
CHLOROftCMZEjME
lilil-TRICHLOftOETHAHE
lil-DICHLOROCTHAHE
CHLOROFORM
l>3-TRANB-ItlCHLOHOETHrLENC
EIHYLBENIENE
HETHYLENE CHLORIDE
TETRACHLOROETHVLENE
TOLUENE
TRICHLOROETHYLENE
2t4t4-TftlCHLpROPHENOL
Itf-mCHLOROPHENOL
PENTACHLOROPHEHOL
PHENOL
ACEMAPHTHENC,,
li2<4-TRICHMJROBENZEHE
lf2-PICH10RO»ENZEHE
l>t-DICHLOROBENZENE
fLUORANIHEHE
NAPHTHALENE.
DIBI2-ETHVLHEXYLI PHTHALAIE
BUTYL DENZYL PHTHALAIE
UI-N-ttUTYL PHTHALATE
01 ETHYL PHIHAIAIE
ANTHRACENE
PHENAMIHREME
PYRENE
ALPHA-ENDOSUI FAN
ANTIMONY
ARSENIC
UNITS
NO/L
MO/L
HO/L
HO/L
UO/L
NO/L
HO/L
ML/L
MO/L
MO/L
MO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
U0/L
INFLUEI
330
244
440
40
•49
980
700
7
312
107
178
22
130
4
2
•42
L 1
17
2
730
9
39
490
4
3
L 1
7
240
N-D
49
1
2
1
20
19
3
4
4
N-D
9
2
2700
4
9
SECOND'
If EFFLUtl
40
19
190
N-B
104
•80
478
L 1
14*
99
14
10
33
1
L 1
2
N-B
19
L 1
3
4
1
14
1
2
1
3
4
2
9
L 1
L 1
N-D
10
2
N-D
1
1
N-0
L 1
N-D
N-D
0
4
MY PCHCEI
If RtMOW
OB
92
77
99»
•a
f
3
•4
33
11
9.1
99
79
03
M
99
•
r
»*
99*
33
97
98
03
33
-
37
9B
.
04
_
90
99*
SO
A7
99*
79
79
-
•0
99*
991
_
20
IT PRIMARY
U. EFFLUCN
270
177
980
24
714
994
997
14
244
40
94
22
120
12
2
29
L 1
11
3
32
4
19
390
•
2
1
4
400
N-D
40
2
2
N-D
23
7
N-0
2
2
N-0
3
N-D
N-D
3
4
PR IN ART
t BLUBOE
29000
31429
47000
7900
1109
42912
1447
929
21770
474
14909
27
1300
N-D
N-D
N-D
•2
N-D
139
143
21
N-D
332
N-D
N-D
N-D
N-D
N-D
N-D
1900
N-D
IBO
140
407
3700
490
440
N-D
380
380
190
N-D
99
180
BEI
•LI
2«(
412
44<
201
20!
44<
17:
90<
294
13:
32<
13
42!
3
N-l
N-l
N-l
3
N-l
9
N-l
14
34
2
N-
N-
N-
N-
N-
33
N-
N-
N-
N-
33
N-
N-
N-
H-
N-
N-
N-l
27
22
;ONDARY
IDOE
to
13
to
t
1
10
13
1
10
13
to
I
1
1
1
>
t
1
POLLUTANTS MOT LISTED UEKE HOT DETECTED AT ANY SAMPLE POINT ON 00/09/21
L'LESS THAN! 0-GKEAIEfi THANI T-TRACE I I OR J-INTERf EftEHCM U'UNCONFIRHEDI
N-D-NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CIIA1TANOOOA
SAMPLE DATE ENtUNO 80/09/21 QBOO HOUftB
FRAC?IOH
NETALB
n
NON-CONV, METALS
PARAMETER
tERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIliE
LEAD
HERCURY
NICKEL
SELENIUM
SILVER
THALLIUM
ZINC
ALUMINUM
BARIUM
frORON
CAICIUN
COBALT
IRON
HAONEBIUH
HANOANEBE
SODIUM
TIN
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
L 1
10
41
»7
9270
MB
L 1000
31
2
14
1
389
9000
113
242
38
L 4»
2330
•
195
23S
42
21
]
L I
SECONDARY
EFFLUENT
L 1
7
23
IB
MS
89
L 1000
78
2
1
1
102
157
24
M4
41
84
313
•
131
248
44
I 2
2
L 3
PERCENT
REMOVAL
•
30
44
Bl
»7
40
-
-
-
94
-
74
93
77
40
-
-
84
-
23
.
-
to
33
-
PRIMARY
EFFLUENT
L 1
II
100
94
4180
143
L 1000
98
3
245
1
834
9740
129
73
43
44
34BO
8
272
212
33
34
7
9
PRIMARY
1LUDOE
230 L
110 L
4900
4400
43800
BtOO
L 10000
1000
I 27
1400
L 13 L
40000
NOT RUN
nor RUN
NOT RUN
NOT RUM
NOT RUH
HOT RUN
KOI RUH
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
•LUDOE
70
14
1300
380
2480
1180
9000
ISO
10
180
9
4900
NOT RUN
HOT RUH
NOT RUN
NOT RUN
NOT RUH
HOI RUN
NOT RUH
NOT RUH
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
POLLUTANTS NOT LISTEU HERE NOT DETECTED AT ANY SAMPLE POINT ON 80/09/21
L'lESS TNANI 0-ORL'ATER THANI I-TRACE! I OR J-INTERFERENCE• U-UNCONFIRHEDt
N-l'-MOr
-------
PAILY ANALYTICAL REBULIS
CHATTAHOOOA
BAHPLE DATE EHDIHO BI/02/JI 0000 HOURB
fftACIIOH
CONVENTIONALB
PARAMETER
ton
TOTAL SUSP
COI>
OIL t CREASE
BOLIPS
o
H
00
ACID EXTRACT
•ASE-NEUIRALB
NON-CONVENTIONALB TOTAL PHtNOLS
TOTAL SOLIDS
TOTAL PISS. SOLIDS
IOIAL VOLATILE SOLIDB
VOlAflLE HI 68. SOLIDS
TOTAL VOL. BUB. SOLIPB
AMMONIA NIIRDOEH
IOC
VOLAT1LEB BENZENE
l.lil-IRICMLOROETHANE
CHLOROFORM
ETIIYLBENZEHE
HETHYLEHE CHLORIDE
TETRACHLOROETHVLCNC
TOLUENE
TRICHLOROErHYLENE
2i4-MCHLOROPHENOL
fEHTACIILOROPHENOL
PHENOL
ACENAPHTHENE
l>2i4-TfllCMlORO»EHZENE
lt3-BICHLORODENZENE
FLUORANTHCNE
NAPHTHALENE
IIB42-ETHYLHEXYL) PHTHALATE
BUTYL BENZYL PHTHALATE
PI-N-iiUTVL PHTHALATE
DIETHYL PHTHALAIE
I>2-ȣNZANTHRACENE
BENZO (A)PYkENE
11f12-BENZOFLUGRANTHENE
CHRYBENC
ANTHRACENE
FLUORENE
CHEN AN HIKE HE
PYfcENE
HETAL6 ANTIMONY
ARSENIC
BERYLLIUM
CAHHIUM
CHROMIUM
POLLUTANTS NOT LIBTEII HERE NOT DETECTED AT ANY BAHPLE POINT ON 81/02/11
L-IES8 TtlANI O'-OfiEAIIR THANI T»TRACEI I OR J-IHTERFERENCE) U-UHCOHFIRHEDf
N-D-NOT tiETECTCD.
UNITS
no/i
HO/L
MO/L
MO/L
UO/L
HO/L
MO/L
HO/L
MO/L
MO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UB/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
210
IS?
120
IB
390
711
932
?34
HO
94
4
IB3
IB
N-P
t«
N-B
440
22
140
4
3
II
10
N-P
H-D
1
N-P
17
IS
N-D
N-P
N-P
N-P
H-P
N-P
N-P
H-b
N-P
N-P
N-P
L 10
L 23
L 1
L 3
2BO
BECONDARY
EFFLUENT
21
17
1*0
7
73
743
724
127
114
1)
3
91
«
N-P
•0
N-P
24
3
II
N-B
2
N-B
170
2
N-P
N-P
N-P
N-D
t
N-D
3
3
H-P
N-P
N-P
N-P
N-D
N-P
N-B
H-D
L 10
L 23
L 1
L 9
70
PERCENT
REMOVAL
.0
•f
30
41
79
.
-
44
If
•A
25
70
*7
-
3B
-
»3
•A
•f
»»•
33
W
-
_
,-
»»»
-
W
40
-
-
-
-
-
-
-
-
-
-
-
.
-
_
-
73
PRIMARY
EFFLUENT
1*0
181
410
13
400
77t
424
191
•4
43
4
IP3
10
N-P
94
»
37
24
130
3
3
N-P
23
N-P
N-D
N-D
N-D
2*
10
H-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
N-P
L 10
L 23
L 1
L 3
3BO
PRIMARY
ILUPOC
7400
37BO
17000
2270
aoo
41BO
3f4
3740
3BO
31BO
12
iaoo
N-D
13
4»
f2
N-D
32
173
19
N-D
N-P
140
N-P
200
N-P
290
200
BIO
300
N-P
N-P
270
700
220
270
30
33
140
140
40
220
30
220
20000
SECONDARY
ILUDOC
2300
3470
»000
403
ISO
3*40
4»2
4040
130
1»30
•
1100
N-D
3
23
N-P
N-P
20
N-P
3
H-P
ISO
N-P
N-B
42
N-D
N-D
27
N-D
N-D
N-D
H-D
N-P
N-P
N-P
N-P
N-P
N-P
N-P
N-P
L 20
eo
30
•0
12000
-------
DAILY ANALYTICAL RESULTS
CHAITAMOOOA
SAMPLE PATE ENDING 81/02/11 OBOO HOURS
FRACTION
NET ALB
NON-CONV. NETALB
O
H
v£>
PARAMETER
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
IINC
ALUMINUM
BARIUM
fiORON
CALCIUM
COS ALT
IRON
HAONEBIUH
MANOANE8E
SODIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
NO/L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
MO /I
UO/L
UO/L
NO/L
UO/L
MO/L
UO/L
UO/L L
INFLUENT
110
3?
97
900
90
4
830
4480
84
10
38
12
4330
4
210
nr
•
s
SECONDARY
EFFLUENT
32
90
L 90
L 300
87
1
120
370
21
77
40
»
170
t
iro
209
L 9
L 9
PERCENT
REMOVAL
71
-
48
40
-
81
84
¥2
79
-
-
29
f2
-
10
-
38
-
PRIMARY
EFFLUENT
f7
81
74
L 300
94
9
320
9110
87
48
40
19
3»eo
4
210
192
7
8
PRIMARY
8LUDOE
9900
934
2700
20000
2700
940
IfOOO
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT R.UN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
SECONDARY
SLUDOE
1200
13
f20
L 10000
980
210
4100
HOI RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
HOT RUH
HOT RUH
NOT RUH
NOT RUH
F-OLI.UIAMTS NOT LISTED HIRE NOT DETECTED AT ANY SAMPLE POINT ON 81/02/11
L-LE9S I HAH I 0-OfcEAIER III AH I I-TRACE I I OR J'lHTERFEREHCEl U-UHCONFIRMED1
N-n-NOt DETECTED.
-------
tiAILY ANALYTICAL RESULTS
CHATTANOOOA
SAMPLE PATE EHHINO BI/02/12 0800 HOURS
FRACTION
COHVENT10NAL6
PARAMETER
• OH
TOTAL SUSP
COD
OIL I OREABE
SOLIDS
n
ACID EXTRACT
BASE-NEUTRALB
NON-CUNVENTIONALS TOTAL PHENOLS
TOTAL SOL 168
TOTAL DIBS. SOLID*
TOTAL VOLATILE SOLIDS
VOLATILE ItlSB. SOL IUS
TOTAL VOL, SUB. SOLIDS
AHHOHIA NIIROOEN
TOC
VOLAIILE6 BENZENE
CHLOftOBENZENE
1tIfI-TRICHLOROETHAHE
CHLOROFORM
ETHYLBENZENE
HETHYLCME CHLORIDE
TEIRACHLOROETHVLENC
TOLUE.ME
TRICHLOROETHrLEHE
2M-DICHLOROFHEHOL
2i4-l»IMETHYLPHENOL
PHENOL
I>2.4-TRICHLOROBEHZ£H£
Itl-PICHLOROBENZENE
FLUORANTHEHE
NAPHTHALENE
HI ETHYL PIITHALATC
DIMETHYL PHTHALATE
1.2-BENZANTHRACENE
BENZO PYRENE
lit12-BEHZOn.UORAHTHENE
CHRV8ENE
ACENAPHTHVLENE
ANTHRACENE
FLUORENE
PHENA.NTHRENE
PTRENE
METALS AHTIHONT
ARSENIC
BERYLLIUM
CADMIUM
CHROHlUn
COPPER
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON BI/O2/I2
L-LES8 THANI 0-OREAIER THANI T-TRACEI I OR J-INTERFERENCE I U'UMCOMFIRMEDI
N-n>NOr DET£CTED<
UNITS
HO/L
HO/L
HO/L
MO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
ul/L
UO/L
UO/L
UO/L
UO/L
UO/L
SECONDARY PERCENT PRIMARY PRIMARY
INFLUENT EFFLUENT REMOVAL EFFLUENT ILUOOE
l»0
11?
310
32
480
7VS
ttt
217
192
•3
*
US
20
N-D
H-D
Be
N-D
240
u
N-D
4
a
M-D
28
N-D
2
N-D
17
»
N-D
N-D
H-D
N-D
N-D
N-D
N-D
N-D
N-D
H-D
L 10
L 23
L 1
L 9
79
•9
20
21
83
4
20
421
*02
• 2
it
U
1
40
1
H-D
N-D
11
N-0
B»
1
N-D
N-D
1
N-P
2
M-D
N-P
H-D
N-B
20
10
N-D
N-D
N-P
N-D
H'P
N-D
N-D
N-D
N-P
L 10
L 23
L 1
L 9
43
18
99
03
74
BB
»»
*2
*
A3
37
• I
•3
74
85
-
.
-
^~
41
92
-
m
40
-
?i
.
m
-
»»«
-
-
_
-
-
_
-
:
.
-
.
-
_
-
40
7»
IBO
101
320
24
480
787
484
IB4
134
32
S
220
23
H-D
N-D
40
23
71
27
440
4
5
2
23
4
3
H-D
19
20
N-D
N-D
N-D
N-D
N-D
N-D
N-D
1
N-D
L 10
L 23
1
L 3
7B
42
12000
27400
24000
4740
400
20400
822
14300
1*0
13*00
14
1*00
10
3
10
78
39
21
40
110
10
N-
H-
N-
H-
N-
90
H-
H-
N-
240
140
240
280
34
140
110
340
420
100
440
180
270
20000
11000
SECONDARY
SLUDOE
2*00
4470
7»00
374
30
7220
948
4B40
ISO
44*0
4
1100
H-
N-
H-
20
3
H-
9
H-
N-
N-
H-
N-
N-
N-
N-
N-
H-
H-
H-
N-
N-
N-
N-
H-
M-
H-
N-
20
too
20
70
7200
too
-------
DAILY ANALYTICAL RESULTS
CHAUAMOOOA
SAMPLE DATE EMDINO 61/02/12 0800 HOURS
n
KJ
FRACTION PARAMETER
HETALB CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
NOM-COMV. METALS ALUMINUM
BARIUM
DORON
CALCIUM
COtALT
IRON
HAONEBIUH
MANGANESE
SODIUM
TITANIUM
VAMADIUH
YTTRIUM
UNITS
UO/L
UO/L L
HO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
MO/L
UO/L L
UO/L
UO/L L
INFLUENT
24
30
300
190
3
3*0
3870
49
41
44
4
3000
7
ISO
ISO
30
s
3
SECONDARY
EFFLUENT
20
L SO
L 300
L 30
1
40
440
22
41
43
4
330
4
ISO
142
S3
L S
L 3
PERCENT
REMOVAL
23
_
L
74
47
83
8V
44
21
2
.
8?
14
21
-
t
-
PRIMARY
EFFLUENT
4V
30
300
V2
4
270
4210
71
74
44
f
3040
7
230
140
30
4
4
PRIMARY
SLUDOE
333
4400
Si 000
4400
330
34000
HOT RUN
HOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDOE
21V
420
L 4000
4BO
130
3400
NOT RUN
NOT RUM
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
POLLUTANTS HOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT ON BI/02/12
L-LES8 THAN! 0*OR£ATER THAN) T'TRACEI I OR J-INTERFERENCEI U-UNCONFIRNEDI
N-D-NOT DETECTED.
-------
PAILT
RESULTS
CHATTAMOOOA
APPITIONAL SAMPLE POINTS
SAMPLE PATE EMPINO BI/O2/I2 OBOO HOURS
FKACTIOH
CONVEMIIONALB
PARAHETER
BOD
TOTAL SUSP. 80LIPS
COP
OIL I ONEASE
NON-CONVENT I ON ALB TOTAL PHENOLS
TOTAL BOLtPS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE PICS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHHOttM NITftOOCM
IOC
ro
VOLATILES
ACID EXTRACT
DASE-NEUIMLS
METALS
COPPER
CTANIPE
LEAP
MERCURY
NICKEL
SILVER
ZINC
NUN-CONV. MEfALfi ALUMINUM
BARIUH
HURON
CALCIUM
HENZENE
CHLOROBENZCNE
1.1-DICHI.OROE1HANE
CHLOROFORM
1>2-TMNB-DICHLOJ)OETHUENE
EIHYLBENZENE
HETHUCNE CHLORIDE
TOLUENE
PHENOL
10-DICHLOROIEN2ENE
1 .2-DIPHEHKLHTKMZINE
NAPHTHA! CNC
• I8(2-ETIITLHEXTL> PHTHALATE
PIETHTL PHIHALATE
ANTHRACENE
FLUORENE
HIEHAMIMREME
I f 2 1 5 . 4-BI tENZAHTHRACENE
CAIlMIUH
UNITS
HO/L
HO/L
HO/L
HO/L
UO/L
NO/L
HO/L
HO/L
HO/L
HO/L
NO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
VACUUM FILTCJ)
FILTRATE
70
410
340
24
244
2010
1400
118
120
198
80
199
1
N-
N-
N-
H-
N-
14
4
PJCES1ER
SUPERNATANT
1100
988
1000
74
43
2210
1440
734
148
144
102
135
13
S»
a
N-D
II
400
11
IfO
L
I
L
L
L
L
L
HATER
1
2
23
2
9
123
128
94
94
2
1
S
i
N-D
N-D
10
N-D
N-D
14
5
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
t.'t/L
111 /L
UO/L
UO/L
UO/L
HO/L
4f
N-D
II
57
7
24
3
I
1
D-D
L 9
120
220
2*
170
1700
110
8
840
11700
100
190
294
13
37
N-D
94
1
21
I
N-D
I
I
4
410
200
14
IfO
1400
140
730
13900
140
170
N-0
N-D
N-D
N-D
N-D
N-D
N-D
N-0
N-D
N-D
L 9
8
10
L 10
L 90
L 100
L 50
L 1
91
23
L 20
21
POLLUTANTS HOI LISTED UfKt NOT PETECTCO l»T ANr SAMPLE POINT ON 81/02/12
L'LESS THAN* 0-OftEATEft THANI T-TRACEI I OR J-INTERFERENCEI U-UNCONFIRMEDI
N-I»HOT PETECTEP.
-------
DAILY ANALYTICAL KEIULTtl
CHATIANOOOA
ADDITIONAL SAMPLE POlttfl
SAMPLE DATE EMM HO 81/02/12 0800 HOURS
FRACTION
NON-CONV. METALS
PARAMETER
CO*ALT
IRON
MAGNESIUM
MAHOANE8E
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
VACUUM FILTER
FILTRATE
DIGESTER
SUPERNATANT
TAP
HATER
UO/L
UO/L
NO/L
UO/L
HO/I
UO/L
UO/L
UO/L
28
»8IO
39
2190
23*
90
13
MO
27
8430
39
22*0
230
SO
10
190
L 9
L 10
3
12
*
44
L S
L S
n
POLLUTANTS HOT LISICD UCRC NOT DETECTED AT ANY BAMPLC POINT ON Bl/02/12
L-LC89 IHANI 0-OREATE* FHANI T-TRACEI I OR J-INTERFERENCE I U-UMCONfIRNEDI
N-II-NOT
-------
DAILY ANALYTICAL RESULTS
CHA1TANOOOA
SAMPLE PATE CNDINO 11/02/11 0800 HOURS
Fit ACT I ON
COMVENTIOMALB
PARAMETER
•OB
TOIAL BUBP
COB
OIL I OREABE
BOLIliB
O
I
to
NON-CONVENTIONALS TOIAL PHENOLS
TOTAL 80LIP8
TOIAL BI8S, BOLIPB
TOTAL VOLATILE SOL1BS
VOLATILE PISS. SOL1BB
TOIAL VOL. SUB. BOLID8
AHHONIA NITROGEN
TOC
VOI.ATILEB
ACIB EXIkACT
BASE-NEUTftALB
METALS
HENUME
CHLOROBENZENE
111 »1-TRICHLOROETHAME
CHLOROFORM
l>2-TRAttB-PICHLOROETHTLENE
ETHTLBENZENE
RETHYLENE CHLORIDE
TE IftACHLOROETHYLEHE
TOLUENE
IRICHLOROETHYLEHE
2i4i4-TRICMLOROFHEMOL
2-CHLOROPHEHOL
2t 4- III CHIOROPIIENOL
PENTACNLOROPHENOL
PHENOL
112. 4'TMCHLORO»ENZEHE
1.2-PICHLOROBEMZENE
1•3-PICHt OROfcENZENE
FLUORAHTHEME
BI8<2-CHLOROETHYOXY> METHANE
NAPHTHALENE
BI8(2-ETHYLHEXYL> PHTHALATE
li2-BENZANTHRACENE
PENZO PYRCNE
II>12-BENZOFLUORANTHENE
CHRYBENE
FLUORENE
PHENANTHHENE
PYRCNE
ANIInOHY
ARSENIC
BERYLLIUM
CADMIUM
BECONDARY PERCENT PRIMARY PRIMARY
UNI 18 INFLUENT EFFLUENT REMOVAL EFFLUENT BLUPOE
MO/L
MO/L
MO/L
HO/L
UO/L
HO/L
MO/L
HO/L
HO/L
MO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
230
27f
seo
73
fso
1140
038
334
174
100
10
219
24
N-P
II
«l
N-P
11
40
IB
uoo
12
1
24
II
9
240
If
N-
N-
N-
N-
N-
3
N-
H-
N-
N-
N-
N-P
N-D
L 10
L 23
L 1
L 3
21
21
100
7
180
734
713
242
224
It
4
44
a
N-P
N-B
2t
N-P
N-P
22
2
130
2
N-B
N-»
N-B
N-D
9
•
N-P
4
N-P
N-P
3
3
N-P
N-P
N-P
N-P
H-P
N-P
N-P
L 10
L 23
L 1
L 3
tl
»2
83
fl
81
33
17
32
-
fl
40
7f
81
-
ft*
32
-
f»»
43
•f
f2
•3
fft
W
ff»
m
fB
38
-
-
-
-
-
40
-
-
-
-
-
-
-
«
-
-
-
310
183
970
40
fOO
lOfO
f04
273
174
f»
f
210
31
N-P
II
44
1
If
70
24
2000
17
N-P
14
f
N-P
87
H-P
9
H-
H-
21
N-
13
N-
N-
N-
N-
N-
N-
N-
L 10
L 23
L 1
L 3
MOO
31000
21000
3420
1400
32000
fSI
13000
270
14700
12
2200
42
7
8
120
N-P
If
N-P
30
2000
.30
N-
H-
N-
N-
N-
8fO
N-P
H-P
180
N-P
340
1300
110
70
130
130
80
170
140
90
440
33
180
BECONPARY
BlUOOE
2700
4340
ffOO
373
179
7130
408
4720
140
4940
f
If 00
9
1
N-B
23
N-B
10
29
9
900
9
N-
N-
N-
N-
N-
40
N-
N-
H-
N-
N-
N-
H-
N-
N-
N-
N-
N-
H-
2O
100
40
100
POLLUTANTS NOT LISTED UEKE NOT DETECTEP AT ANY SAMPLE POINT ON 81/02/13
L-LEE* THANI 0-OREATER TIIANI T-IRACEi I OR J- INTERFERENCE I U-UNCONFIRHEBI
N-P>NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENDINO ai/02/13 0800 HOURS
FRACTION
METALS
NON-COHV. METALS
D
ro
PARAMETER
CHROMIUM
COPPER
CYANIDE
LEAD
HERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
IORON
CALCIUM
COBALT
IRON
NAONEB1UH
MANOANESE
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L
UO/L
INFLUENT
79
40
21
L SO L
L 300 L
76 L
7
370
4990
80
AS
49
*
3240
7
300
214
L 90
• L
L 9 L
SECONDARY
EFFLUENT
40
IT
31
90
300
90
1
120
430
24
40
49
9
330
7
190
20f
«7
9
9
PERCENT
REMOVAL
4f
48
-
L
I
34
•4
48
91
70
•
-
17
«0
-
37
3
-
3B
-
PRIMARY
EFFLUENT
100
42
»2
SO
300
72
4
300
9720
89
90
SO
9
3080
B
290
230
98
8
7
PRIMARY
BLUDOE
12000
9800
1240
3100
23000
3400
4BO
23000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDGE
8800
1200
248
770
L 10000
740
180
4400
HOT HUH
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT ON 81/02/11
L-LE8S IHANI 0>OREATER THANI 1-TRACEI I OR J-INTERFERENCEI U-UNCONFIRHCDI
H P-NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATIANOOOA
SAMPLE PATE E Nil I NO 81/02/14 OBOO HOURS
FRACTION
CONVENT IONALS
PARAMETER
BOD
TOTAL SUSP.
COD
OIL I OREASE
SOLIDS
NUN-CONVENTIONALB TOTAL PHENOLS
TOTAL SOLIDS
TOTAL UI88; SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE D188. SOLIDS
TOTAL VOL. SU8. SOLIDS
AMMONIA NITROOEN
TOC
VULATILES
ACID EXTRACT
BASE-NEUTRALS
HETALS
BENZENE
CHLOROBENZENE
Ii1i1-TRICHLOROETNANE
CHLOROFORM
l>2-TRANS-r>ICHLOROETHYLENE
ETHYLDEHZENC
NETNYLENE CHLORIDE
IETRACNLOROETHYLENE
TOLUENE
IRICHLOROETHYLENE
2-CIILOROPHENOL
2i4-DICHLOROPNENOL
2>4-|HHE1HYLPIIENOL
PHENOL
l>2i4-TRICKLOROBENZENE
li3-DICHLOROBENZENE
l.4-[iJCHLQKO«fNZEHE
FLUORANTHENE
4-CHLOROPIIENYL PHENYL ETHER
NAPHTHALENE
0IB<2-ETHYLHEXYL> PHTHALATE
PI-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
DIMETHYL PHTHALATE
11 2-IlENZANTHfcACENE
Hi 12-BENZOFLUORANTHEHE
CllfcYBENE
ACENAPHIHTLENE
ANTHRACENE
FLUORENE
PHEHANTHftEME
PYRENE
ANTIMONY
UNITS
MO/L
HO/L
NO/L
no/L
UO/L
HO/L
NO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UB/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
SECONDARY PERCENT PRIMARY PRIMARY
INFLUENT EFFLUENT REHOVAL EFFLUENT SLUDGE
30ft 44
24V 21
74ft 03
82
6
1300 60
83
V2
8V
V3
V9
1250 8V4 20
VV8 871 II
zee n* sv
144 104 37
124 19
10
0
300 97
a
3
ea
20
81
73
N-D N-0
8
60
1
16
43
ia
N-D VV*
30
30
N-B VV»
N-K W
28
4
140 13
a
i
H-
4
4
6
M-
N-
N-
1
IB
78
VI
68
N-D VV»
P 2
2
4
-
30
-
N-0 »»•
P N-
D N-
P M-
N-0 N-
13
H-
2
P H-
N-D N-
H-P N-
N-
P N-
N-P N-
N-
H-
H-
N-
P H
P N-
P N-
P N-
M*P N-
M-P N-
N-P N-
-
-
-
-
83
-
-
-
-
-
-
-
-
_
-
-
280
173
330
43
1210
1244
1070
341
2BO
83
10
240
7
N-P
V
SA
2
17
40
23
130
a
N-P
N-D
N-D
130
13
1
2
1
-D
-P
0
3
-P
-P
N-P
4
1
N-P
1
1
10000
43400
28000
3040
1400
44400
1170
18400
240
18200
IV
3000
10
3
10
73
N-P
30
N-P
40
430
10
N-D
N-P
N-P
360
740
N-P
N-P
140
120
260
N-0
N-P
1100
N-D
N-0
N-0
N-P
N-fr
N-0
34
140
120
SECONDARY
SLUDGE
2600
7210
8300
327
ISO
7VOO
688
4780
180
4600
10
2200
2
N-D
N-D
V
N-D
2
N-D
N-D
V
IS
N-D
N-D
N-D
N-D
60
N-D
N-D
120
N-D
N-D
2
N-D
N-D
N-D
66
40
60
N-D
44
N-0
40
H-0
UO/L L 10
L 10
L 10
130
40
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT OH 81/02/14
I-LESS THAN I 0-OHEAIEh I HAH I T-TRACEI I OR J-INTERFERENCE • II-UNCONFIRHEDI
N-b^NOT DETECTED.
-------
DAILY ANALYTICAL REBULI8
CHATTANOOGA
8AHFLE PATE ENDINO 81/02/14 0800 HOURS
TRACTION
METALS
n
NOK-CONV. HETALB
PARAMETER
ARSENIC
DERYLLIUM
CADMIUM
CHROH1UN
COPPER
CYANIDE
LEAD
HERCURV
NICKEL
8ELENIUH
SILVER
ZINC
ALUNINUH
•ARIUH
•OR ON
CALCIUM
CODALT
IRON
MAGNESIUM
HAMOANESC
SUCllUM
TITANIUM
VANADIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L
INFLUENT
L 29
L 1
L S
130
SO
tie
L SO
•00
100
L 23
10
420
MOO
110
120
4*
•
4240
a
140
281
L 30
7
SECONDARY
EFFLUENT
L 23
L 1
L 3
120
ft
34*
L 30
L 100
77
L 23
1
140
4*0
23
UO
44
9
•30
•
210
271
37
L 3
PERCENT
REMOVAL
_
-
-
•
4
-
-
43
n
-
TO
47
T3
77
-
4
-
•0
-
3S
4
_
2»
PRIMARY
EFFLUENT
L 23
L 1
L 3
110
44
177
L 30
L 300
04
L 23
»
140
7480
f3
130
4»
f
3300
f
310
2»»
L 30
L 3
PRIMARY
SLUDOE
1200
•9
210
23000
7700
402
4SOO
10000 L
4100
40 L
350
IfOOO
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDOE
110
13
100
••00
1100
111
1100
10000
• 40
30
210
4*00
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT ON 81/02/14
L-U88 tHANt 0-OREATER THAMI T-TRACEI I OR ^INTERFERENCE! U-UNCONFIRNEDI
N-D-NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE PATE EHUINO 01/02/13 0800 HOURS
FRACTION PARAHEIER
CONVENTlOHAti »OD
TOTAL BUBP. BOLIDS
COD
OIL I OREASE
NON-CONVENTIONALB TOTAL PHENOLS
T01AL SOLIDS
TOTAL DIBS. BOLIDS
TOTAL VOLATILE BOLIDB
VOLATILE DIBS. BOLIDB
TOTAL VOL. 9U*. BOLIDB
AMMONIA NITROGEN
TOC
00
VOLATILCB
ACIU EXTRACT
HASC-NEUTRAIS
HETAL8
•CNIENE
CHLOROBENZENE
I>1II-TRICHLOROETHANE
1•1>2-TRICHLOROETHANE
CHLOROFORM
li2-TRANB-OICHLOROETHYLENC
EIHYLBENZENE
METHYLCHE CHLORIDE
TETKACHLOROETHYLENE
TOLUENE
TfilCHLOKOEIHYLENE
2i4-DICHLOROPHENOL
PHENOL
l>2t4-TRICHLORODENZENE
FLUORANIHCME
NAPHTHALENE
BIB<2-ETHYLIIEXYL> PHTHALATE
DIEIHYL PHTHALATE
ACENAPHTHYLENE
ANTHRACENE
PHENANTHRENE
ANTIMONY
ARSENIC
KEKYLLIUH
CAPHIUN
CIIKOMIUM
COPPEft
CYANIDE
LEAD
NICKEL
SILVER
ZINC
UNITS
MO/L
HO/L
HO/L
MO/L
UO/L
HO/L
HO/L
NO/L
HO/L
HO/I
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L L
UO/L L
UO/L L
UO/L
UO/L
UO/L
UO/L L
UO/L
UO/L
UO/L
INFLUENT
ISO
ISA
3*0
30
1130
1240
1000
2»»
110
II*
17
280
»
N-B
9
H-D
33
M-II
N-D
HO
21
220
10
2
410
N-D
N-D
II
1
4
1
1
1
10
29
1
3
140
ao
if
30
44
2
230
SECONDARY
EFFLUENT
40
22
140
7
•0
1010
1000
914
970
14
10
74
2
N-0
H-D
N-i
31
N-D
2
47
4
20
1
1
20
H-
N-
N-
II
H-
N-
H-
N-D
L 10
L 29
L 1
L 9
34
42
43
L 30
30
1
120
PERCENT
REMOVAL
74
•4
74
77
»1
17
7
-
-
80
41
71
70
-
m
-
40
-
-
44
• 1
»l
40
30
»s
-
-
w
»»«
»»«
w
»»«
_
-
-
-
74
47
-
-
12
30
48
PRIHARY
EFFLUENT
2tO
112
440
21
1400
1240
1110
141
278
81
14
310
10
2
7
N-0
4f
2
17
100
12
290
29
1
900
H-0
N-0
31
N-0
N-D
N-D
N-D
N-D
L 10
L 29
L 1
L 9
210
4*
34
L 90
L 30
3
220
PRIHARY
8LUDOE
1000
20300
17000
2040
1730
21400
1140
12000
300
11700
IB
1800
10
N-D
0
N-D
*r
N-D
90
N-D
4*
173
13
N-D
300
N-D
40
100
N-
N-
H-
N-
H-
40
430
13
100
0300
4700
410
2*00
2200
240
18000
SECONDARY
ILUDOE
843
4480
*000
94*
118
7280
5*3
1970
180
11*0
17
720
N-
N-
N-
4
2*
N-
N-
H-
8
1*
3
N-
H-
40
N-
N-
N-
H-
N-
N-
N-
40
1*0
28
40
7*00
1100
101
•30
810
210
1*00
POL1UTANTB NOI LISTED UERE HOI DETECTED AT ANY SAMPLE POINT ON 81/02/19
L-LEBS THANI 0-OREATER THAN! !•TRACE I I OR J'lHICRFEREMCCI UMJHCOHFIRNEDI
N-D-NOI DETECTED.
-------
DAILY ANALYTICAL kESULTB
CHATIANOOOA
SAMPLE DATE ENDINO 11/02/15 0100 HOURS
FRACTION PARAMETER
MON-COHV. NETALB ALUNINUN
•ARIUH
»ORON
CALCIUM
COBALI
IRON
MAOHEBIUH
NANOANE8E
BODtUN
TITANIUM
VANAUIUH
YTTRIUM
UNI 19
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L L
UO/L L
INFLUENT
2410
71
110
44
4
I BOO
T
270
241
41
3
9
SECONDARY
EFFLUENT
9JO
24
130
44
•
440
»
240
27T
L SO
L 9
L 9
PERCENT
REMOVAL
00
44
-
-
74
-
II
-
IB
-
-
PRIMARY
EFFLUENT
4090
fl
too
S3
•
2080
10
110
292
41
9
9
PRIMARY
SLUDOE
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
SECONDARY
SLUDGE
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT RUH
HOT RUN
NOT RUH
HOT RUN
ro
vo
POLLUTANTS NOT LIBIEO HERE NOT DETECTED AT ANY SAMPLE POINT ON 01/02/19
L-IC93 TMANI O'OREATER IHAMJ T-FftACEl I OR J«INTERFERENCE I U-UNCONFIRNEDI
M-I.-MOT PETCCTEIt.
-------
DAILY ANALYTICAL RESULTS
CHATIANOOOA
SAMPLE DAIE ENDING 01/02/14 0100 HOURS
FRACTION
CONVENTIONAL II
PARAMETER
ftOD
TOTAL BUBP.
COB
Oil I OREASE
SOL I 118
?
ACID EXTRACT
BABE-NEUTRALS
HON-tONVENIIONALB TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIS8. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI8S. SOLIDS
TOTAL VOL. 8US. SOLIDS
AMMONIA NITROOEN
IOC
VOLATILE8 »EMIEME
I.1,1-1R1CHLOKQE THANE
CHLOROFORM
I>2-TRAN8-DICHLOROETHYLEHe
CTHYLDENZENE
METIIYLENE CHLORIDE
TETKACIILOROETHYLENC
101 UENK
IRICmOROCIHYLEME
2.4-DICHLOROPHENOL
PEHIACHLOftOPHENOL
PHENOL
ACEHAPHTHENE
I>2>4-TR1CIILORODEHZEHE
l>3-OICHLOkODEN2EME
FtllOKANTHENE
ftIB(2-CHLOKOe!HYOXY» METHANE
NAPHTHALENE
DIB(2-CTHVLMEXYL> PHTHALATE
ACENAPHTHYLENE
FLUOfcENE
PHEMANTHRENE
NETALB ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAU
MEttCUHY
NICKEL
SILVER
POLLUTANTS HOI LISTED HERE NOT DETECTED AT ANY SAMPLE POINT OH 01/02/14
L-IESS THANI 0-OREATER THAN I I-TRACE I I OR J-INTERFERENCE I U'UNCONFIRHEDI
N-Ii-NOJ DETECTED.
UNITS
NO/L
NO/L
MO/L
HO/L
UO/L
NO/L
NO/L
HO/L
HO/1.
NO/L
NO/L
MO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L L
UO/L L
UO/L L
UO/L
UO/L
UO/L
UO/L
NO/L L
UO/L L
UO/L
INFLUENT
144
144
340
19 L
730
7S1
417
in
104
»2
it
140
12
a
34
2
»
21
12
270
•
3
N-D
210
1
4
2
N-D
It
21
»
2
N-D
N-D
10 L
29 L
1 L
a L
2*
9*
111
00 L
300 L
90
2
SECONDARY
EFFLUENT
24
17
130
2
13
747
730
lit
ioa
ii
•
4B
1
H-D
10
N-D
N-D
020
N-D
IS
N-D
N-D
N-D
9
N-D
N-D
N-D
N-D
H-D
N-D
H-D
N-D
N-D
H-D
10
29
1
9
28
HO
14
90
300
170
1
PERCENT
REMOVAL
02
00
42
• 7
*4
a
-
40
-
00
27
44
79
m
12
• f»
»»l
—
w
»4
»»»
W
-
t4
»>»
»»»
»»«
-
»»»
»>»
»t»
m
-
-
_
-
-
-
i
-
70
41
-
-
9ft
PR I NARY
EFFLUENT
190
fl
400
ai
1000
749
472
104
114
90
13
149
IV
•
94
2
21
49
20
410
11
9
N-D
230
N-
N-
N-
M-
N-
30
N-
H-
N-
N-
L 10
L 29
L 1
L 9
97
99
13
L 90
L 300
L 90
2
PRIMARY
SLUDOE
IfOO
14100
13000
9940
1190
14000
4*4
• 4fO
140
0110
24
1400
19
10
ito
N-D
41
N-D
32
440
12
H-D
20
200
N-D
140
N-D
140
N-D
100
N-D
N-D
40
100
80
040
39
100
10000
4400
409
3400
10000
2700
240
SECONDARY
8LUDOE
040
92SO
7400
909
41
9000
999
1790
190
3400
17
430
N-D
N-D
20
N-D
N-0
N-D
3
11
N-D
N-D
N-D
N-D
N-D
92
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
20
120
21
40
4400
1100
IfO
4*0
L 10000
710
100
-------
DAILY ANALYTICAL RESUL1B
CHATTANOOOA
SAMPLE PATE ENDING 81/02/14 0800 HOURS
SECONDARY PERCENT
FRACTION
METALS
NON-CONV, HETALS
n
Ul
PARAMETER
ZINC
ALUMINUM
•ARIUN
BORON
CALCIUM
COSALT
IRON
MAGNESIUM
NANOANESE
BODIUN
TITANIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
00/L
NO/L
UO/L
UO/L
NO/L
UO/L
NO/L
UO/L
UO/L
INFLUENT
ISO
3S?0
82
74
48
a
2310
•
310
147
L SO
L 9 L
EFFLUENT
200
380
2*
73
4*
t
380
9
250
l?4
«l
3
REMOVAL
-
Of
*•
1
-
-
83
-
1*
-
-
-
EFFLUENT.
ISO
3480
77
37
32
t
2100
10
390
ISA
L SO
»
SLUOOE
17000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT HUH
HOT RUN
BLUDOE
3fOO
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
POlLUtANTS NOT LIBTCH UERE NOT DETECTED AT ANY SAMPLE POINT ON 01/02/U
l-LESS THANI O'GREATER MIAMI T-TRftCEl I OR .('INTERFERENCE» U-UNCONFIRHEDI
N-I»NOr PETCCIEn.
-------
DAILY ANALYTICAL KEBULIB
CHATTANOOOA
8AMPLE DATE ENDING 11/02/17 0000 HOUKtt
fit ACT I ON
COMVEMT1ONALB
n
u>
N>
PAKAHEfER
MID
TOTAL BUSP. SOL IPS
COO
OIL I UREASE
NON-COHVCN1IOHALB TOTAL PHENOLS
TOIAL SOLIbB
TOTAL HUB. SOLIDS
TOTAL VOLATILE BOLID8
VOLATILE DIBB. SOL IPS
TOTAL VOL. SUB. SOLIDS
AHHOMIA NITROGEN
TOC
UNITS INFLUENT
SECONDARY PERCENT
EFFLUENT REMOVAL
HUN Aft*
EFFLUENT
PRIMARY
SLUPOE
SECONDARY
•LUPOE
VOLAI1LEB
ACIP EXTRACT
VASE-NEUTRALS
rc&iicmes
MCIALS
•ENIENE
CHLORUtEMZEHE
lilil-TRICHLOROETHANE
Irl-DICHLOKOETHANE
l>lt2>2-TETRACHLOROETHANE
CHLOROFORM
I»2-TRANB^DICHLOROETHYLENE
ETIIYLBEHZEHE
HETIITLEHE CHLORIPE
TETRACHLOIiOETHrLEHE
TOLUENE
TRICHLOROETHYLEHE
2t4-DICHLOROPHEMDL
PHENOL
ACENAPHTHENE
l>2i4-TRICHLOROBENZENE
HEXACIILOROETHANE
I.J-DICHLOROBENZENE
11 4-DICHLOROkENZEHE
2>4-PIMITROTOLUEME
FLUURAHTIIEME
BIB(2-CHLOROETHYOXY» METHANE
NAPHTHALENE
BIB<2-ETHYLHEXYL> PHTHALATE
DI-H-BUTYL PHTHALATE
ACCHAPHTMYLENE
ANTHRACENE
FLUCMEME
PHEHANTHRENE
PYRENE
ALPHA-tHC
ANIIHONY
HO/L
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
2BO
244
too
49
*00
1140
10»0
374
222
152
10
260
20
N-D
7
H-D
N-D
120
N-D
34
23
38
900
10
2
2*0
I
•
N-D
2
4
N-D
N-D
20
N-D
140
N-D
3
I
2
I
N-D
N-D
UO/L L 10
2*
2*
110
3
33
Oil
7B2
141
124
17
•
41
4
N-D
N-D
H-D
H-D
43
H-D
3
22
2
33
N-D
N-D
B
N-
N-
M-
N-
N-
N-
3
N-
N-
N-
N-
N-
N-
H-
N-
N-
N-D
L 10
to
6B
• 2
t3
»4
3»
2B
42
44
•r
20
B4
BO
ft*
11
9t
12
»S
Bf
fVt
w
2»0
177
a»o
40
•oo
1320
1140
137
23B
71
10
240
IB
N-D
112
N-D
N-D
130
1
4»
24
34
400
13
I
210
N-D
7
N-D
1
4
H-D
H-D
N-D
13
3
I
N-
N-
N-
H-
N-
N-D
L 10
14000
24400
34000
8390
1130
27700
lOtO
12100
120
11 BOO
If
4200
20
4
N-D
f
10
73
N-D
170
N-D
N-D
430
270
N-D
440
40
480
40
N-D
H-0
40
140
N-D
240
N-D
N-D
N-D
220
BO
140
120
BO
B3
2700
4740
7200
370
100
7440
4*4
2430
1BO
2430
17
1400
H-
N-
N-
N-
N-
39
N-
N-
N-
10
H-D
2
N-D
N-D
N-D
40
N-
N-
N-
H-
N-
N-
N-
H-
H-
N-
N-
H-
N-
N-
N-D
34
POILUtANTS NOT LISTED WEKE NOT DETECTED AT ANY SAMPLE POINT ON BI/02/I7
L'LESS IHAN> O^OfiEATEfc THAN! T-TRACEI I OR J-INTERFEDENCEI U*UNCONFIRHEDI
N-[»NOr DETECTED.
-------
I'AILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE PATE ENDING 81/02/17 0800 HOURS
U>
U>
FRACTION PARAMETER
METALS ARSENIC
tCRYLLItlH
CAPHIUH
CIIROHIUH
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
ZINC
NON-CONV. METALS ALUMINUM
»ARIUN
»ORON
CALCIUM
COIALT
IRON
MAGNESIUM
HANOANEBE
SODIUM
VANADIUM
YTTRIUM
UNITS INFLUENT
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
L 10
L 1
9
140
»3
134
?2
1000
SB
12
10
970
L
L
L
L
L
L
L
SECONDARY PERCENT
EFFLUENT REMOVAL
10
1
9
23
20
13
90
300
90
10
1
110
_
-
-
82
79
70
44
70
14
17
»0
81
L
L
L
L
L
PRIMARY PRIMARY SECONDARY
EFFLUENT SLUDGE SLUDOE
10
1
s
110
64
140
Of
1200
30
10
•
900
2300
100
280
18000
10000
2720
• 300
90000
4700
40
»»0
37000
410
24
40
4000
1200
»2
»20
L 8000
800
L 30
200
4200
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L L
9840
130
190
90
13
3910
f
320
308
9
9
440
2V
120
47
9
420
8
240
238
L 9
I 9
f2
78
20
4
42
88
II
29
23
9140
140
120
47
II
3130
a
300
319
L 9
7
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOt RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUIANTB HOI LI8IED WERE NOT DETECTED AT ANY SAMPLE POINT ON 81/02/17
I-LESS MIAMI 0-OREATER THANI f'TRACEl I OR J-INTERFERENCEI U'UMCONFIRHEbl
N-II-MOI
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENDING 81/02/10 OBOO HOURS
FRACTION
CONVENTIONAIH
PARAMETER
•OD
TOTAL SUSP
COD
OIL I OREAHE
SOL I PS
NON-CONVENTIONAL8 TOTAL PHENOLS
TOIAL SOLIDS,
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE D188. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
VOLAT1LE8 HEMZENE
I»I»I-TRICNLOROETMANE
l»l-PICHLOftOETHAHE
I.I<2-TRICHLOROETHANC
CHLOROFORM
Irl-PICHLOROETHYLENE
ETHYLDEMZENE
HETHYLENE CHLORIDE
TETRACHLOROETHYLEHE
TOLUENE
TRICHLOROETHYLENE
2>4-DICHLOROPHENOL
2r4-PinETHYLPHENOL
4-NITROPHENOL
PHEHOL
ACENAPHTMENE
lr2»4-YRICHL6KOBCNZEHE
11 3-DICm.ORDIENZEHE
FLUORANTHENE
*ia<2-CHIOROETHYOXY> METHANE
NAPHTHALENE
tI8<2-ETHYLHEXYL> PHTHALATE
•UTYL BENZYL PHTHALATE
P(-N-»UIYL PHTHALATE
FLUDRENE
PHENAMIIIKENE
PYRENE
HETALB ANTINOMY
AHBENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
POLLUTANTS NOT LISTtfc UCKE NOT DETECTED AT ANY SAMPLE POINT ON 81102/18
L«LES8 THAN* Q-GKErtUK THANI I'TRACEI I OR J» INTERFERENCE I U'UNCONFIRHEDI
N-P-NOI DETECTED.
ACID EXTRACT
BASE-NEUTRAL*
UMIT8
MO/L
MO/L
MO/L
MO/L
UO/L
MO/L
MO/L
HO/L
Mfl/L
HO/L
MO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L L
UO/L L
UO/L
UO/L
UO/L
INFLUENT
220
U2
410
li L
400
844
702
249
170
»3
4
110
27
240
H-D
N-D
44
21
21
S3
21
J»0
10
14
N-D
N-D
120
N-D
21
1
N-U
14
17
4
N-D
H-D
N-D
N-P
N-D
10 L
10 L
1 L
3 L
54
74
SECONDARY
EFFLUENT
2*
24
120
2
•4
•44
030
lit
102
17
S
SI
4
34
N-D
N-D
42
1
10
40
4
28
2
3
1
N-P
4
M-0
2
3
N-D
H-D
N-D
2
H-D
2
N-D
H-D
N-D
10
10
1
3
28
13
PERCENT
REMOVAL
07
•4
71
•*
•2
-
-
33
40
•2
17
72
•3
77
-
-
-
»3
32
27
74
*J
•0
7*
-
-
9J
_
to
-
.
• *»
m
30
-
-
-
-
-
L
L
L
-
90
81
PRIMARY
EFFLUENT
240
141
420
21
480
»21
740
204
128
78
3
1VO
28
H-D
N-D
210
81
8
37
71
33
3*0
12
13
N-D
N-D
140
N-0
21
N-0
N-P
N-D
20
10
N-D '
N-P
N-D
H-D
N-P
10
10
1
3
7*
at
PRIMARY
SLUDOE
12000
2*400
27000
2840
713
10300
1120
17*40
240
17700
7
4000
N-P
2300
13
N-P
fO
N-P
H-P
N-P
90
4*0
33
N-P
N-P
H-D
N-D
38
720
N-D
110
N-D
310
N-D
H-P
N-P
70
200
110
2V
800
24
210
4400
4300
SECONDARY
SLUPOE
4*00
4f*0
•400
471
18
73*0
400
2420
120
2300
3
3200
12
40
N-P
N-P
17
N-D
4
N-D
N-D
H-D
3
H-D
H-D
400
N-D
H-D
120
H-D
H-D
H-D
40
N-D
1000
N-D
H-P
H-D
N-D
24
230
32
PO
3300
1300
-------
DAItY ANALYTICAL RESULTS
CHATIAHODOA
SAMPLE VATC END1NO BI/02/1B OBOO HOURS
FRACTION
METALS
HON-CONV. METALS
PARAMETER
Ln
CVANIUE
LEAP
HERCURY
NICKEL
BILVER
IINC
ALUMI NUN
BARIUM
•ORON
CALCIUM
COBALT
IRON
MAONEBIUH
HANOANE8E
80PIUN
VANADIUM
YTTRIUM
UNITS
OO/L
00/L
NO/t
UO/L
OO/L
UO/L
UO/L
UO/L
UO/L
NO/t
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L
INFLUENT
41
a?
L 300
L 90
4
290
3320
•9
7»
42
21
3090
4
220
19V
L S
L 9
SECONDARY
EFFLUENT
44
L 90
L 300
L 90
1
130
440
2*
too
40
•
420
7
200
294
L 9
L 9
PERCENT
RENOVAL
_
43
-
-
79
33
07
4»
-
9
*2
04
-
»
-
-
-
PRIMARY
EFFLUENT
17
77
300
49
4
330
3030
f7
• 9
4
20
2*80
7
240
1*1
7
4
PRIMARY
SLUDGE
440
4100
40000 L
2700
710
29000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
8LUDOE
30
1100
•000
t30
230
«VOO
NOT RUN
NO! RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
F-OLLUTAMTB NOT LISTED UCRC NOT DETECTED AT ANY SAMPLE POINT ON B1/02/IB
L-LESS THAN I O'OfttATEK THANI T'TRACEI I Oft J-IHTERFERENCEI U-UNCONFIRNEDI
N-D-MOT (tETCCTED,
-------
DAILY ANALYTICAL RESULTS
CHAT1ANOOOA
ADDITIONAL 6AHPLE POINI8
BAHPLE [>ATE END1NO 01/02/10 0800 HOURS
FRACTION
CONVENTIONALB
PARAMETER
HOP
TOTAL SUSP
COII
OIL I OREA8E
SOLIDS
to
NON-CONVENTIONAL8 IOTAL PHENOLS
TOTAL SOL I US
TOTAL DISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE PISS. SOLIDS
TOTAL VOL. 6U8. SOLIDS
AHHON1A NITflOOEH
TOC
VOLATILES
ACIP EXTRACT
KASE-NEUTRAL 8
HtTALS
VENZENE
CHLOROBEHZENE
ItI-PICHLOROETHANE
CHLOROFORM
lt2-TRAHB-DICHLOROETHYLEHE
ETHYL BENZENE
HETHYLENE CHLORIDE
Dl CHLOROfROHOHE THANE
TOLUENE
PARACHLOROHETA CRE60L
2-CHLOROPHENOL
2>4-CICHLOHOPHEHOL
PHENOL
1<1-DICHLORODENZENE
I>4-DICHLORO(ENZENE
1>2-DIPHENYLHYDRAZINE
NAPHTHALENE
NITROBENZENE
»IB(2-ETHrLHEXYL) PHTHALATE
BI-M-*UTYL PHTHALATE
METHYL PHTHALATE
ANTHRACENE
PHENANTIIRENE
CADMIUM
CHROHIUH
COPPER
LEAb
HERCURY
NICKEL
SILVER
ZINC
UNITS
HO/t
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
VACUUM FILTER
FILTRATE
42
444
220
a
279
mo
1340
224
110
»4
40
123
2
N-D
H-D
N-D
N-D
H-D
7
N-D
a
H-D
1
1
7
N-P
N-D
1
1
N-D
4
N-D
2
H-D
H-D
L a
130
37
94
700
L SO
1
290
PIOESTER
SUPERNATANT
110
124
910
21
940
I4SO
1140
400
224
174
44
i»o
f
22
*
N-D
7
110
1
N-D
100
]
N-B
N-D
»
17
3
H-D
N-D
24
9
2
N-D
1
1
4
420
270
240
1100
140
It
flO
TAP
HATER
L 1
L 2
L 29
4
L 9
129
129
90
90
L 2
L 1
4
2
H-D
N-D
42
N-D
21
9
2
4
N-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
H-D
N-D
2
H-D
H-D
N-D
L 9
12
L 10
L 90
L 300
L 90
L 1
13
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY BAHPLE POINT OH SI/02/18
L-LE8S THAN* 0-OREATER THANI T-IRACEI I OR J-INTERFEREHCEI U'UNCONFIRHEDI
N-D-NOT DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTAHOOOA
ADDITIONAL SAMPLE POINTS
SAMPLE PATE ENDING 81/02/18 0800 HOURS
to
FRACTION PARAMETER
NON-CONV. HETALS ALUMINUM
MRIUH
80RON
CALCIUM
COIALT
IRON
MAONESIUH
MANGANESE
MOLriDENUN
SOPIUN
TITANIUM
VANADIUM
YTTRIUM
UNITS
VACUUM FILTER
FILTRATE
DIGESTER
SUPERNATANT
TAP
HATER
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
MO/L
UO/L
44«0
170
ISO
282
Id
S2IO
17
2240
UO/L L 10
MO/L 232
UO/L L 90
UO/L 7
UO/L 10
17*00
410
120
211
IS
11100
28
21*0
14
177
210
It
120
as
21
L 20
24
L 3
180
4
L 10
L 10
8
L 30
L 3
L 9
PQLLUIANIS NOT LISTEli HERE NOT DETECTED Al ANY SAMPLE POINT ON 01/02/16
L-LESS THANI 0-GRCATCK MIAMI T-TRACfl I OR J-INTERFERENCE I U»UNCONFIRMEDI
N-D-Nnr DETECTED.
-------
DAILY ANALYTICAL RESULT*
CHATTANOOOA
SAMPLE PATE tHU I HO 81/02/1* 0600 HOURS
FRACTION
CONVENTIONAL*
PARAMETER
BOD
I01AL SUSP.
COO
OIL I ORCABC
iOLIDB
U)
00
NON-CONVENTIONALS TOTAL PHENOLS
TOTAL SOLIDS
IOIAL DIBS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI8S. SOLIDS
TOTAL VOL, BUS. SOLIDS
AHHONIA NITROGEN
IOC
VULATILE8 fENZENE
I>111-TRICHLOROE THANE
Itl-ftlCHLOROETHANE
I>Ii2>2-TETRACHLOROETHANE
CHLOROFORH
li2-TRAHS-DICHLOROETHVLENE
ETMVLBENZENE
HETMYLENE CNLORIDE
TE TRACIIL OHOE THTL ENE
TOLUENE
IRICHLOROETHYLENE
2>4i4-TRICHLOROPHENOL
2>4-DICIILOROPHENOL
2>4-DINITROPHENOL
PENTACHLOROPHENOL
PHENOL
ACENAPHTHENE
I•2i4-TRICHLOROBENZENE
111-DICHI ORODENZENE
li4-DICHLORODENZENE
FLUORANTHENE
DI8I2-CHIOKOISOPROPYL> ETHER
NAPHTHALENE
DI8I2-ETIIYLHEXVLI PHTHALATE
DI-N-BUTYL PHTHALAIE
(I I ETHYL PHTHALATE
PHENANTHKENE
PYRENE
HEIALS ANTIHONY
ARSENIC
BERYLLIUM
CAPHlUn
CHKoniun
POLLUTANTS NOT LISTED WLRE NOT DETECTED AT ANY 8AHPLE POINT ON 81/02/lf
l-IISS IHAH I 0-ORCATEK THANI T'TRACEI I Oft J-lNTERFERENCEl U-UNCONF1RHEDI
N-b'NOT PETECTtD.
ACID EXIRACT
BABE-NEUIRALB
UHII8
HO/L
HO/L
NO/L
HO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L '
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UG/L
UO/1.
UO/L
UO/L
UO/L
UO/L
UO/L
UU/L L
UO/L L
UO/L L
UO/L L
UO/L
•El
IMFLUEHI CFI
ISO M
121 2»
290 tl
3 4
190 11
471 87.
390 34
l»7 44
124 49
71 21
3 1
130 IB
2* 2
10 4
H-D N-l
B N-
41 11
N-D N-l
IB N-l
47 44
430 IV
13« )
7B N-l
N-P 4
B 4
N-B N-
N-D N-
100 2
» H-
9 N-
I N-
1 N-
N-D H-
N-D N-
4 N-
1 22
1 N-
2 N-
N-ll N-
H-B N-
10 L 10
10 L 10
1 L 1
3 L 3
90 79
CONIiARY PERCENT
FLUEHI REHOVAL
ft
77
44
20
94
I 13
1 1
44
44
70
BO
71
»2
40
)
II »»»
2B
1
> W
11
74
»»
1 »f»
_
23
•
-
VB
»f»
»»«
»»*
»*«
-
-
W
-
»»+
»»»
-
-
L
L
L
L
-
PMIHAHY
EFFLUENT
110
*4
140
II
120
474
37B
147
fa
4V
3
129
27
II
N-D
M-0
4B
1
40
43
VO
380
4
N-D
II
14
3
B?
41
9
4
N-0
N-D
3
N-»
4
2
N-B
N-»
N-D
10
10
1
9
100
PRIMARY
BLUDOE
12000
2VSOO
22000
1210
411
10100
740
14700
220
14300
7
1100
30
20
7
N-B
40
N-D
80
N-D
230
490
120
N-D
N-0
N-D
N-D
H-»
N-D
22O
H-»
N-D
BO
N-D
80
N-D
N-D
N-D
80
40
94
V40
280
1*0
10000
SECONDARY
BLUDOE
3000
4110
7200
1340
L-B
4800
470
4140
70
4270
3
1100
N-D
N-
N-
H-
H-
N-
N-
N-
80
N-
N-
N-
N-
N-
N-
N-
N-
10
N-
N-
N-
N-
H-
N-
N-D
N-D
N-D
N-D
14
100
42
70
4000
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENDING BI/02/1? OBOO 1*0 UK 8
FRACTION PARAMETER
n
METALS COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
NON-CONV. METALS ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
NAONES1UH
HANOANEBC
SODIUM
VANADIUM
YT1R1UH
UNITS
UO/L
UO/L
UO/L
HO/L L
UO/L
UO/L
UO/L
INFLUENT
43
17
84
300
200
4
230
L
L
L
SECONDARY
EFFLUENT
10
17
30
300
95
1
93
PERCENT
REMOVAL
7B
40
L
32
73
42
PRIMARY
EFFLUENT
41
24
33
300
180
2
210
PRIMARY
6LUDOE
8100
1300
7400
24000 L
MOO
330
31000
SECONDARY
BLUDOE
1300
203
1200
BOOO
1300
230
4900
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
NO/L
UO/L
HO/L
UO/L
UO/L
4440
72
34
42
17
2400
4
220
122
3
10
340
28
41
41
14
440
4
100
137
L 3
L 3
87
2
18
73
18
30
3T70
47
120
43
14
2040
4
210
114
L 9
22
NOT RUN
NOT RUN
HOT RUM
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
POLLUTANTS NOT LISTED UtfcE NOT DETECTED AT ANY SAMPLE POINf ON 81/03/1?
"'*"' f"TRACE' ' OR J-'NTERFERENCEI U-UNCONFIRMED*
-------
DAILY ANALYTICAL KESULti
CHA1TANOOOA
SAMPLE DATE ENPINO 81/02/20 OSOO HOUR*
FRACTION
CONVENTIONAL 8
PARAMETER
HOD
TOTAL BUBP,
COD
OIL 1 CREASE
SOLIDS
O
I
ACID EXTRACT
»A8C-MEUTRAL8
NON-CUNVENT10NALB TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI9B. SOLIDS
TOTAL VOL. BUS> SOLIDS
AHHONIA NIIROOEM
TOC
VOLATILE! ICNZENC
I>1.I-TRICHLOROEINANC
CIILOROFORN
li2-TRANB-DJCHLOROCTIIYLEHE
ETHYLBENZENE
HETHYLEHE CHLORIDE
TEIRACHLOROCTHYLENE
TOLUENE
TRICHLOROETH1TLENE
2r4-DICHLOROPHENOL
2>4-01HETHYLFHENOL
PHENOL
l>2f4-IRICHLORODENZENE
lt2-DICHLOKOBENZENE
I.3-DICHLO*0»ENZENC
I>4-DICHLOROBENZENE
FLUORANTHEHE
»I8<2-CHLOROI80PROPTLI ETHER
NAPHTHALENE
N-NIIROSODIPHENYLANINE
»IS<2-EniYLHEXri> PHTHALAIE
DI-N-DUTYL PHIHALATE
DI-N-OCTVL F-HTHALATE
DIEIHTL PHIHALATE
ANTHRACENE
PIIENANTHREME
HETAL8 ANTINOMY
ARSENIC
BERYLLIUM
CAHHIUN
CHROtuun
COPPER
CYANIDE
POLLUTANTS NOI LISUI> WERE NOT DETECTED AT ANY SANPLE POINT UN 01/02/20
L'LESS IHANI 0-OKEAIER TIIANI T-IRACEI I OR J-INIERFERENCEI U-UNCOHFIRNEDI
N-I'-NOI I'ETECIEP.
UNITS
HO/L
HO/L
NO/L
NO/L
UO/L
MO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUE
290
178
4JO
*
500
01*
ASS
234
1S2
102
9
143
t
4
9t
H-D
3»
»o
114
79
1
7
H-D
yi
it
N-D
2
21
H-D
H-B
1
N-D
2
2
N-D
H-B
H-D
N-D
L 10
L 10
L 1
L 9
41
48
III
SECOND*
NT EFFLUEI
22
»*
170
I
19
702
40*
141
82
44
1
98
i
N-0
34
N-D
4
41
21
1
H-»
2
1
4
7
29
H-D
H-B
H-D
N-D
N-D
H-D
«
10
If
4
N-D
N-6
L 10
L 10
L 1
L 9
. **
17
29
>RY fence
IT REhOV
?l
44
40
90
f7
U
8
42
44
13
40
43
47
m
42
-
»1
34
82
*4
W
71
-
f4
94
-
W
m
-
-
m
-
-
.
-
•
-
-
_
-
.
-
-
49
77
0
t
>0
)
10
)
0
>0
I
>
to
>0
-------
hAILI ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE PATE CNIUNO 81/07/20 OBOO HOURS
FRACTION
PARAMETER
MEIALS LEAD
MERCURY
NICKEL
SILVER
IINC
HON-COMV. HEIALfl AtUHINUH
SARIUN
IUROH
CALCIUM
COBALT
IKON
HAONESlUn
HANOANEBE
SODIUM
VAN A HI UN
units
UO/L L
NO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
INFLUENT
SO
100
130
4
220
4710
77
130
41
U
Jl»0
7
290
144
S
SECONDARY
EFFLUENT
I 30
L 300
90
2
130
mo
34
too
44
14
1420
4
210
130
L 3
FERCCMt
REMOVAL
_
-
92
30
J2
sr
30
23
-
11
38
14
14
-
-
PRIMARY
EFFLUENT
L 90
L 300
•a
4
180
IfOO
73
ISO
44
4
2V40
7
230
133
L 3
PR 1 HART
SLUDOE
4300
14000 L
17000
400
24000
HOI RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDGE
770
•000
1200
230
4400
HOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
rotLUIANTS NOT LISTED UERE NOT DETECTED AT ANY SAMriC POINT ON SI/02/20
L-LES9 TIIANI G'OREATFR THAN) l-IRACfl I OR J-INTERFERENCE» U-UMCONFIRHEDI
N Ii.NOT tiETEtTEIi.
-------
DAILY ANALYTICAL RESULTS
CHATTAMOOOA
SAMPLE DATE EHPINO ai/«2/21 0800 HOURS
FRACTION
CONVENT I DUALS
PAKAMEIEK
ton
TOTAL 8U8P,
COD
OIL I GREASE
sot IPS
NON-CONVENTIONAL8 TOTAL PHENOLS
TOTAL SOLIt8
TOTAL DIBS. SOLIDS
IOIAL VOLAI1LE SOLIDS
VOI ATIL£ HISS. SOLIDS
TUTAL VOL. BUS. BOLIDS
AHHONIA NITROGEN
IOC
VULAIILE6 HENZENE
I.1.1-IRICHL OROE THANE
Itl-DICHLOROCTHANE
I>Ii2-TKICHLOROCTHANE
CIILUNOFORH
1.2-TRAHS-DICHLOftOETHaENE
EIHT1DENIENE
HETIirLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TKICHlOROETIirLENE
VINYL CHLORIDE
2>4-DICHLOROPHENOL
2f4-DIHETHYLPI|ENOL
PHENOL
I>2»4-IRICHLORO»ENZENE
Itl-DICHLOROBENZENE
li4-MCIILORUHLMZEHE
NAPHIIIALENE
II8I2-ETHYLHEXYL) PHTHALATE
DI-N »UTYl PHIIIALAIE
IIIETIirL HHTHALATE
ANTHRACENE
fHENANIURENE
METALS ANTIHONY
ARSENIC
•LRYLLIUH
CAOnlUN
CIIROHIUH
COPPER
CYANIPE
LEAD
MERCURY
POILUIANIS NOT LI6IEII UEhE NOT DETECTED AT ANY SAMPLE POINT ON 81/02/21
L-I.ISS THAHI O-OREATER THAHI T-TRACEI I OR J-INTERFERENCE I U-UNCONFIRMEbl
M-Ii-HOl DETECTED.
ACID EXTRACT
BASE-NEUTRALS
UNITS
NO/L
NO/L
HO/L
HO /I
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
SECONDARY PERCENT PRIMARY PRIMARY IECONDART
IHfLUEMT EFFLUENT REMOVAL EFFLUENT BLUDQE ILUPOE
210
Ul
ISO
M
400
• 11
448
247
144
101
•
133
12
4
H-D
M-D
90
1
II
120
46
79
3
N-D
4
N-D
77
40
4
N-D
24
3
14
U
1
1
L 10
L 10
L 1
L 3
120
43
207
L 30
400
22
21
f7
L 2
21
704
474
111
»4
22
9
41
3
N-
«-
N-
29
N-
N-
40
7
3
H-D
H-D
1
2
13
U
1
N-P
N-D
1
4
4
N-D
N-D
L 10
L 10
L 1
L 9
23
L 10
10]
L 30
L 300
to
•1
72
84
9t
13
-
32
33
7f
31
74
73
W
-
-
42
m
m
90
82
»4
»»»
-
73
-
• 1
60
23
-
»»*
eo
73
43
9»»
W
.
-
-
-
81
84
90
-
23
iao
104
340
II
790
822
718
201
132
4f
f
149
IS
18
N-D
N-D
34
2
12
200
34
100
4
N-D
4
N-8
110
37
N-D
3
N-D
3
10
18
2
2
L 10
L 10
L 1
L 9
110
42
344
44
L 300
9400
21400
21000
1810
1000
22300
too
11800
240
11300
21
4300
8
N-0
3
IS
39
8
13
10
14
83
19
3
N-P
N-P
300
180
N-0
N-D
40
H-
N-
N-
N-
N-
23
1100
28
180
3*00
4100
278
2400
34000
1472
4000
4fOO
303
43
4330
930
4030
120
3730
II
?40
N-D
N-b
N-
N-
20
N-
N-
N-
13
N-
N-
N-
N-
N-
N-
12
N-
N-
N-
N-
N-
N-
N-
N-
43
210
13
70
3100
1200
173
1000
L 8000
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENDING 01/02/21 0800 MOORS
FRACTION
METALS
PARAMETER
NICKEL
SILVER
ZINC
NON-CONV. METALS ALUMINUM
BARIUM
•ORON
CALCIUM
CO*ALT
IROH
HAONEBIUH
MANGANESE
SODIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
INFLUENT
4?
4
230
4100
100
110
49
If
3120
4
270
1*1
JO
SECONDARY
EFFLUENT
L 90
1
120
940
33
ts
4«
l<
420
«
200
179
L 9
PERCENT
REMOVAL
29
79
92
•7
47
29
-
14
a?
_
24
-
79
PRIMARY
EFFLUENT
78
4
200
24«0
fl
120
4V
23
1040
7
240
U4
17
PRIMARY
SLUDOE
10000
330
uooo
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDOE
1300
240
4200
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LIBIED WIRE NOT DETECTED AT ANY BAHFLE POINT ON 01/02/21
L-LESS THAftl 0*OftEATCft THAN) T-TRACEI I Oft J-INTERFERENCEI U-UNCONFIRHEDI
H-|i»MOT t'EUCfED.
-------
HAILY ANALYIICAL RE 801 IS
CIIAITANOOOA
8AHPLE t'ATE ENDING 81/02/23 0*00 HOURS
FRACTION
CONVENTIQNAL8
PARAMETER
• Oil
TOTAL SUSP
COD
OIL I OREA6E
SOLIDS
NON-CONVENT IONAL8 IOIAL PHENOLS
(DIAL. SOLIDS
IOIAL PISS. SOLIDS
IOTAL VOLATILE SOLIDS
VOLAIUE 1-188, SOLIDS
IOTAL VOL. BUS. SOLIDS
AHHON1A NIIROOEN
IOC
-P-
VOLAIILE8
ACID EXIRACI
BASE NEUTRALS
BEN2ENE
till I -TRICMLOROETHANE
CHLOROFORM
lr2-TRAN8-PICHLONOETHYLENE
ETimUFNZENE
HETHYLENE CflLORIPE
HEIIIVL CHLORIDE
I E IK ACM. OROE THYLKNE
UIIUENC
IRICIILOROETHVLENE
2r4-DICMLOROPHEHOl
PHENOL
lt2>4-TRlCHLOROii£NZENE
Irl-DICIILOROBENZCNE
!>4-DICH1.0RO(iENZ£NE
li2~Il|PHEHYLHT»RAZIN£
FlUORAHTHENE
NAPHTHALENE
t>IK<2-ETHYLHEXYL> PHTHALAIE
DI-M-fiUIYL PHTHALATE
miflHENE
PMENANTHftCME
PYKENE
ANT1HONY
ARSENIC
KERT1LIUH
HtlALS
ciiKoniun
COPPER
CYAHlliE
LEAH
HEKCURY
NICKEL
POLLUIAMIS NOT LI8IEU UEKE NOI DETECIfD AT ANY SAMPLE POINT OH 01/02/22
I-'IESS THAN* 0"GREATt'K IIIANI T-TRACEI I OR J-IHTERFERCNCE* U-UHCONFIRHCDI
N-D»NOI titucrr.li,
UNITS
NO/L
HO/L
HO/L
HO/L
UO/L
no/i
MO/L
HO/L
HO/L
HO/L
MO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/I
UO/L
UO/L
UO/L
UO/L
NO/L
UO/I
INFLUENT
IVO
219
110
11
• 70
•a*
474
111
uo
• S3
10
199
14
/
3»
1
II
110
N-0
II
100
«
I
190
M-V
N-D
N-D
4
M-»
13
1
9
M-P
M-D
N-D
L 10
L 10
L 1
L 9
9*
94
15
L 30
3OO
L 30
SECONDARY
EFFLUENT
11
21
90
9
11
477
43*
104
80
1*
t
27
1
N-D
20
N-D
N-D
30
N-D
2
4
M-»
1
2
N-D
N-D
N-
N-
N-
N-
N-
N-
N-
N-
M-
L 10
L 10
L 1
L 9
24
L 10
42
L SO
I 100
L 30
PERCENT
REMOVAL
VI
»0
84
42
99
11
4
47
43
to
10
8]
»1
W
91
W
991
33
-
82
t*
99t
47
99
_
-
-
m
-
m
w
99t
-
-
-
_
-
-
-
79
81
-
-
4O
-
PRIMARY
EFFLUENT
190
00
240
10
870
314
414
140
104
34
10
119
14
9
41
1
19
N-D
71
IB
110
4
1
190
0
2
N-D
N-0
N-D
24
M-0
N-D
H-D
N-D
N-D
L 10
L 10
L 1
L 9
IV
21
22
L 90
i. 100
t 30
PRIMARY
SLUDGE
/800
19400
1*000
1800
1190
14300
830
10000
290
10300
27
4400
IB
N-D
29
N-D
IB
ISO
N-D
7
120
a
N-D
470
740
N-D
44
N-D
140
220
N-D
N-D
40
140
120
29
1200
24
120
8100
4400
319
3100
90000
4300
SECONDARY
BLUIiOC
2800
4810
4300
233
IB
3290
480
1330
120
1210
37
2100
N-D
N-D
18
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
40
N-D
N-D
H-D
H-D
N-D
H-D
N-D
N-D
N-D
N-D
29
170
22
30
4100
1000
241
490
10000
1100
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE HATE END1NO BI/02/22 0800 HOURS
FRACTION PARAMETER
METALS SILVER
ZINC
NON-CUNV. NETAL8 ALUMINUM
BARIUM
BORON
CALCIUM
CODALT
IRON
HAONESIUH
MANGANESE
MOLYBDENUM
SODIUM
VANADIUM
YTTRIUM
UNIIS
UO/L
UO/L
INFLUENT
6
220
SECONDARY
EFFLUENT
1
110
PERCENT
REMOVAL
83
30
PRIMARY
EFFLUENT
I
ISO
PRIHARY
BLUOOE
S20
1BOOO
SECONDARY
BLUDOE
220
3300
UO/L
UO/L
UO/L
HO/L
UO/L
un/L
MO/L
UO/L
UO/L L
HO/L
UO/L
UO/L
1080
100
130
4»
14
2780
4
320
10
48
9
7
340
31
8B
4»
10
320
4
230
L 10
104
L 3
L 3
88
*»
32
2V
8B
28
I9BO
71
7»
91
10
1470
7
100
10
84
L 9
L 9
HOI RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
Ul
POLLUTANTS NOT IISUI" UEKE NOT I'ETECTEli AT ANY SAMPLE POINT ON 81/02/22
L-IESS THANI 0«OREATCR THAN* T-TRACEI I OR J-INTERFERENCEI U'UMCONFIRHEDI
N-D-NOT RETECTEO.
-------
DAILY ANALYTICAL RESULTS
CMATrANOODA
SAMPLE DATE £NOINO 01/02/2] 0800 HOURS
FRACTION
COMVENIIONALS
PAKAMEIER
• Oil
TOTAL SUSP
COb
OIL I OREA8E
SOLIDS
NUN-CONVENTIOHALB 101AL PHENOLS
TOTAL SOLIDS
TOTAL 0188. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE 1H88. BOLIt'B
TOTAL VOL. BUS. SOLIDS
AHHONIA HITROOEN
IOC
VOLATILES
ACID EXTRACT
kASE-NEUTKALS
»EN1ENC
CIILOft.O>ENZENE
l>t>l-TRICIILOROETHANE
CHLOROFORM
lt2-IRAH8-PICHLOROETHYLENE
ETIIYLBEN1ENC
METHYLCNE CHLORIDE
TETRACtlLOROETHYLENE
TOLUENE
TRlCHLOftOETHVLENC
2»4-DICMLOROPHENOL
PCNTACHLOROPIIENOL
PHENOL
ACEHAPHTHENE
li2i4-TftICHLPRO*EHZCNE
HEXACHLOROtENZENE
2-CHLORONAPHTHALEMC
li4-DICHLOKOIlENZENE
1.3-IUPHENYLMrDRAZIME
FLUURAHTHCME
li|8U-CMLOROETHYOXY> METHANE
NAPHTHALENE
IIIBI2-ETHYLIICXVLI PHTIIALATE
»UTYL hENZYL PHTHAIATE
bl-N-HUTYL PHIHALATE
METHYL PHIHALATE
l>2-nNZAMTHRACEME
CIIRYSENE
ACENAPHTHTLENE
ANTHRACENE
PHENAHTHRENE
PYRfNC
UMITS
NO/L
HO/L
HO/L
HO/L
UO/L
MO/l
HB/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UD/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
IVO
101
200
13
330
3B»
484
1 74
110
44
1?
130
13
H-D
N-D
37
1
21
31
12
HO
10
N-D
N-D
220
N-D
N-0
N-D
N-D
N-D
N-D
N-D
8
10
12
N-
N-
N-
H-
N~
N~
H-
N-
N-
N-
SECONDARY
EFFLUENT
10
18
44
13
8
414
3*4
»4
78
14
ts
31
1
N-D
4
18
H-D
N-D
14
1
3
4
1
1
1
N-
H-
N-
N-
N-
N-
M-
N-
N-
18
N-D
7
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
PERCENT
REMOVAL
»3
81
77
II
»r
30
19
47
2t
74
12
74
92
-
-
33
fM
W
33
92
*4
40
.
-
»t»
_
-
-
-
-
-
-
99t
m
-
-
-
-
-
-
-
.
-
-
-
PRIMARY
EFFLUENT
140
72
200
t
420
930
478
If 4
144
30
IS
113
14
2
7
37
1
22
120
11
180
9
a
N-P
140
3
2
1
1
N-D
3
1
to
14
34
7
4
1
N-8
2
N-0
3
3
N-D
3
PRIHAftY
8LUDOE
9200
10700
17000
4870
too
11300
410
7700
300
7400
23
1100
IB
N-D
N-D
20
N-D
40
N-D
13
230
20
N-D
N-D
N-D
N-D
140
N-D
N-D
40
N-D
120
N-8
240
N-D
N-D
N-D
N-D
N-D
N-D
7
N-D
40
100
100
SECONDARY
8LUDOE
214V
4230
3200
121
38
4430
400
2370
'100
2470
23
JfOO
N-D
N-D
N-D
13
H-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
H-D
N-D
80
H-D
N-D
N-D
N-D
N-D
N-D
40
40
40
N-D
N-D
N-D
80
POLLUIAHIS NOT LISTED UEfcE NOT DETECTED AT ANY SAMPLE POINT ON Bl/02/23
L-LESS THANI 0-OHEAIth THANI T«TRACEI T OR J-INTERFERENCEi U*UNCONFIRHEDI
N-n-NOI liETECTEb.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOOA
SAMPLE tiATE ENDING 81/02/23 0000 HOURS
FRACTION PARAHETER
NETALS ARSENIC
bERYLLlUH
CADMIUM
CMRUHIUH
COPPER
CYANIDE
LEAD
NERCURY
NICKEL
SILVER
ZINC
NON-CONV, NETALS ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
MAONEBIUH
MANGANESE
MOLYBDENUM
SODIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
INFLUENT
t
L
L
L
L
10
1
9
24
24
12
90
400
90
2
220
L
L
L
L
L
L
I
L
L
SECONDARY PERCENT
EFFLUENT REMOVAL
10
1
9
10
10
12
30
300
30
1
32
.
-
-
42
42
-
-
29
-
90
74
L
L
L
L
L
PRIMARY PRIMARY SECONDARY
EFFLUENT 8LUDOE SLUDOE
10
1
9
27
IS
IS
97
300
30
|
110
120
23
22
1400
1200
IBS
930
30000
8»0
110
4BO
74
B
80
3900
840
134
440
L 10000
1100
130
3100
UO/L 2970
UO/L 49
UO/L B9
NO/L SI
UO/L •
UO/L 1720
MO/L 7
UO/L 310
UO/L 43
MO/L 100
270
30
74
90
10
240
4
240
L 10
74
94
19
2
84
14
14
84
24
IB20
40
92
94
10
1080
7
310
94
99
HOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUfAHfS NUt LI91EI. WERE NOI DETECTED AT ANY SAMPLE POINT ON 81/02/23
L-I.ESS rilANI 0*GREAILK THANI T-TRACEI I OR J-INTERFERENCE I U-UNCONFIRHEDI
N-II-NOT IICTECIED.
-------
HAILY AHALYTICAL KESULIB
CHATTANOOGA
UAMPLE HATE ENDIHO 81/02/24 OBOO HOURS
FRACTION
L'OMVtNflONAi.S
PARAHtltR
«UK
10IAL SUSP
COP
Oil. I CREASE
SOLIliS
NON-CONVENTIOHAL8 TOTAL PHENOLS
TOTAL SOL IPS
10IAL DIBS. BOLIDB
TOTAL VOLATILE SOLIDS
VOLATILE [lisa, SOLIDS
10TAL VOL. BUS. SOLIDS
AMMONIA HITROOEN
TOC
VOLATILEB
00
ACID EXTRACT
»ASE-NEUTRALB
HETALS
DENZENE
I > 111-1RICHLOROE THANE
1«I.2-1RICHLOROETHANE
CHLOROFORM
ETHY1DEHZENC
HETHYLFHE CHLORIDE
TETkACHLOROETHYLENE
TOLUENE
IRICHLOROEIHYLEHE
2i4-DIHITHOPHEHOL
PHENOL
ACEHAPHIHEHE
I>2>4~TRICHL4ROBENZENE
DtB(2-CIILOROETHYL) ETHER
lr2-MCIILOROBEHZEHE
1.3-IUCIUOkObEMZENE
1.4-DICHLOKOkENZENE
Fl UORAMTHENE
BI8(2-CHLOROETHYOXY> METHANE
NAPHTHALENE
BIS(2-EIHYL)IEXYL) PHI HAL A IE
HI N-fcUIYL PHTHALATE
PIETHVL f-HIHALATE
lr2-DENZANIH)(AC£NE
11.12-DENZOFLUORANIHENE
CHRYSEHE
ACENAPHTHYLENE
ANTHRACENE
FLUURENE
PHENAHIHRENE
PYREHE
ANTIMONY
ARSENIC
UMiia
MO/L
HO/L
HO/I
HO/L
00 /L
MO/L
MO/L
HO/L
MO/L
MO/L
MO/L
MO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L,
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L
SECONDARY fCfcCEMI PRIMARY PRIMARY SECONDARY
INFLUENT EFFLUENT REMOVAL EFFLUENT SLUPOE SLUDOE
330
23*
700
20
320
1370
1110
32»
174
199
19
280
12
U
H-D
80
9
3*
4f
230
290
«
.lao
2V9
49
N-D
N-P
4
•
N-D
N-D
20
4
4
N-
M"
N-
H-
N-
N-
2
N-
N-
11
L 10
30
23
110
L 2
39
•41
820
82
70
12
U
48
3
1
N-D
2f
1
71
7
11
5
N-D
8
N-D
7
N-D
N-D
2
H-D
N-D
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
9
If
VI
VI
84
VO
8V
38
24
79
40
V2
-
83
79
81
-
44
80
-
8*
va
ve
w
V4
vvt
•4
-
-
90
vvt
-
-
vvt
vvt
vvt
-
-
-
-
-
-
vvt
-
-
99
-
270
14V
400
IV
320
I2BO
1130.
280
1V4
84
14
24B
V
8
N-0
3B
27
ISO
42
ISO
14
3
N-D
N-D
18
I
N-D
1
2
N-D
27
N-D
4
1
1
N-D
H-D
N-D
3
N-D
1
H-D
N-D
II
L 10
14000
20300
24000
1130
VOO
21700
1370
II BOO
390
11400
34
4VOO
13
10
8
VO
49
N-D
110
300
23
N-D
N-D
N-D
1400
N-0
100
H-D
240
340
N-D
440
N-D
N-0
N-0
80
40
•0
N-D
200
•0
280
300
110
2300
3000
4BIO
4300
2VO
• 8
9730
V20
3430
120
3310
20
leoo
N-
N-
N-
N-
N-
N-
H-
N-
N-
N-
N-
N-
44
H-
N-
N-
N-
N-
N'
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
L 30
100
POLLUTANTS NOT LISTED UEKE NOT DETECTED AT ANY SAMPLE POINT OH Bl/02/24
L-U83 111 AH I 0-OftEAUK THANI I'TRACE I I OR J-IHTERFERENCCI U'UNCONFIRNEDI
N-K-HOI DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHAITAMOOOA
SAMPLE DATE ENDING BI/02/24 0800 HOURS
TRACTION PARAMETER
O
*-
VO
METALS BERYLLIUM
CADMIUM
CHRONIUN
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
ZINC
NON-CONY. METALS ALUMINUM
BARIUH
•OR ON
CALCIUM
COtALT
IRON
MAUNE8IUN
MANGANESE
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
INFLUENT
L I
9
210
130
VO
L 90
300
VI
L 10
4
940
4030
140
HO
91
21
2700
•
340
3V
323
44
9
10
SECONDARY
EFFLUENT
L I
L 9
30
24
40
SO
L 300
70
L 10
1
110
440
10
09
SO
1?
330
a
220
42
234
L 9
L 9
L 9
PERCENT
REMOVAL
L
L
• 7
BO
94
I
-
23
L
•3
•0
V2
7V
3V
4
24
BB
-
39
-
27
V2
-
90
PRIMARY
EFFLUENT
1
9
220
V4
127
90
300
74
10
7
1VO
9230
ll»
130
94
29
2210
V
310
31
313
Jl
9
10
PRIMARY
•LUDOE
31
VO
VIOO
1400
1000
•80
40000 L
470
40 L
290
4900
HOT HUH
NOf RUN
NOT RUN
NOT RUN
NOf RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDOC
IS
VO
4VOO
1300
2V7
410
10000
V70
40
210
4400
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LI81ED UEKE HOT DETECTED AT ANY SAMPLE POINT ON BI/02/24
i-iESs THAN* O-ORCATER IIIANI T-TRACEI i OR .(-INTERFERENCE* U-UNCONFIRHEDI
N D--NOI DETECTED.
-------
HAIIY AHALVIICAL KE8UIIS
CIIATIAHOOOA
ADDITIONAL SAMPLE POINTS
SAMPLE HATE EHD1HO 81/02/24 0100 HOURS
FRACTION PARAMETER
n
U1
o
CONVENT JONALS HOD
TOTAL SUSP. SOLIDS
COD
OIL I OREABE
NON-CONVENUOHALtt TOTAL PHENOLS
TOIAL 801 IDS
TOTAL DUB. SOLIDS
TOIAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
101AL VOL. HUB. SOLIDS
AMMONIA HIIftOOEH
TOC
VOLAIILE8
AC|[> EXTRACT
DASE-NEU1RALB
kENZEHE
CMLORODENZENE
CHLOROFORM
I ,2-TRANB-DICHLOROETHYLEHE
ETHTLDEHZEME
MCTHUEHE CHLORIDE
TOLUENE
PHENOL
ACENAPHTHENE
lil-DICHlOkOBENZEHE
1.4-UICHtOKOIENZENE
I!8<2-CHLOROETIIYOXV) HETHAHE
NAPHTHALENE
BIKI2-ETIIYLHEXYLI PHTMALATE
GI-N-fctmL PIITHALATE
DI-N-OCITL fHIHALATE
DIETMTL MITHALATE
ACENAPIIItlYLEHE
ANTHRACENE
PHENANIIIRENE
I>2I9>«-UIDENZANIHKACENE
METALS ARSENIC
DERTLLIUH
CADMIUM
CHROMIUM
COPPER
CVANIHE
LEAD
MERCURY
NICKEL
SILVER
POLLUTANTS NOT LISTED HtRE NOT DETECTED AT ANY SAMPLE POIHT OH 81/02/24
LM.ESS IHAHI OMIREAIEft IHANI I-TRACEI I OR J- INTERFERENCE > UMIMCOHFIRHEOI
N-D*NOT DETECTED.
UNITS
HO/L
HO/L
HO/L
HO/L
UO/L
NO/L
MO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
VACUUM FILTER
FILTRATE
110
273
110
9
240
1920
1240
170
140
10
90
?3
3
N-D
H-D
H-D
3
10
a
V
H-D
N-D
N-D
1
N-D
4
N-D
N-D
3
27
H-D
N-D
N-D
H-D
L 10
L 1
L 8
34
49
L 10
L 30
L 100
SO
1
DIOEBTER
SUPERNATANT
290
f 4f
1100
120
940
2280
1110
728
2t4
412
130
439
f
20
K-D
21
220
9
120
H-D
9
27
3
3
20
84
7
9
19
H-D
8
4
1
t
12
1
10
430
280
11
240
400
270
12
TAP
HATER
L 1
2
L 29
L 2
L a
82
80
98
98
L 2
L 1
4
1
H-D
21
N-D
N-D
4
4
H-D
H-D
H-D
N-0
N-D
N-D
3
H-D
H-D
H-D
H-D
H-D
H-D
H-D
H-D
L 10
L I
L 3
L 10
24
L 10
L SO
L 100
L 30
L 1
-------
DAILY ANALYTICAL RESULTS
CHATTANOOOA
ADDITIONAL SAMPLE POINTS
B AMP It DATC ENOINO BI/02/24 0800 HOUH8
FRACTION
METALS
PARAMETER
ZINC
UNITS
VACUUM FILTER
FILTRATE
DIGESTER
SUPERNATANT
TAP
MATER
UO/L
100
O
HON-CONV. NETALB ALUMINUM
•ARIUM
•DRON
CALCIUH
COVALT
IKON
HAONESIUH
NANOANCSC
MOLYBDENUM
9001 UN
TITANIUM
VANADIUM
YTTRIUM
UO/L t?90
UO/L 130
UO/L 170
NO/L 270
UO/L 11
UO/L 4420
HO/I 3«
UO/L 2910
UO/L L 10
NO/L 224
UO/L 21
UO/L L 9
UO/L 0
1080
22100
4SO
ISO
301
41
isaoo
3*
3430
IS
23S
77
20
140
32
L 40
22
L 20
22
9
120
4
L 10
L 10
10
L 9
L 9
L 9
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT OH 01/02/24
L-LESS TMAN1 0-OREATEft THANI T-TRACEt I OR J-INTERFERENCEI U-UNCONFIRHEDI
N-D-NOI DETECTED.
-------
BAILT ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE HATE ENDIHO BI/02/29 0800 HOURS
FftAC IION
CONVENTIONAL8
PARAMETER
BUD
TOTAL SUSP.
COO
OIL I OREASE
SOLIDS
n
Ui
to
HUH CONVENTIOHALB IOTAL PHENOLS
TOTAL iOLIOS
TOTAL DIBS, SOLIDS
TOtAL VOLATILE SOLIDS
VOLATILE DI8S. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITKODEN
TOC
V01AIILCB
AblU EXTRACT
BASE-NEUTRALS
METALS
VEN2EHE
IiI.I-IBICMLOROETHANE
1>I>2-TRICHLOROETHANE
CHLOROETHAHE
CHLOROFORM .
li2-TRANa-DICHLOROCTHYLEHE
ETHYLBENZENE
HETHYIENE CHLORIDE
TEIRACHLOROETHYLENE
TOLUENE
TRICHLOftOETHYLENE
2,4,4-TRlCHLOROPHEMOL
2>4-DINIIIt0PHEHOL
PENTACIILOROFHENOL
PIIENQI.
ACEHAPHTHEME
1.2,« TMCMLDROMNJENE
I>1-DICHLUROBENZENE
lf4-I>ICHLOROBENZEHE
FLUORANIHENE
VIS(2-CHLOf ETHER
»|8<2-CHLOKOETHYOXY> METHANE
NAPHTHALENE
*IS(2-EUIYLIIEXYL> PHTHALAIE
*UTYL BENZYL PHTHALATE
DI-N-BUTYL PHTIIALATE
OI-H OCTYL PHTHALATE
(METHYL PHIilALAIE
ACENAI-HIIIYLENE
FLUOKEME
PHENANIHKENE
ANTIMONY
AKSENIC
UNITS
NO/L
NO/I
NO/L
NO/L
UO/L
NO/L
NO/L
NO/L
NO/L
HO/L
NO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/i
JO/L
UO/L
UO/L
UO/L
SECONDARY PERCENT PRIMARY PRIMARY SECONDARY
INFLUENT EFFLUENT RENOVAL EFFLUENT SLUDOE SLUDOE
130
211
490
24
730
11*0
900
141
220
121
17
279
10
a
N-D
N-D
90
N-»
41
13
43
2*0
17
N-D
I
«
110
220
44
2
3
N-D
H-D
»
2*
4
H-D
0
H-D
17
H-D
2
H-D
11
L 10
3*
40
IBO
3
43
1020
t7B
too
*B
12
12
7t
3
N-B
N-D
N-B
12
H-B
*
27
9
24
SB
N-D
N-B
N-D
3
N-D
14
2
N-B
N-D
H-D
4
H-D
N-D
H-D
N-B
N-D
27
H-D
H-D
H-D
*
L 10
B4
• 1
74
7»
fl
14
-
71
4*
74
2V
71
12
W
m
-
44
-
to
_
B4
to
-
.
W
f»t
93
f»»
70
-
»»»
-
-
BB
W
»t»
-
W
-
-
-
W
-
43
-
110
I7J
700
21
B70
1140
ffO
274
144
112
IB
290
10
3
H-D
H-B
31
1
H-D
It
41
H-D
42
1
I
2
110
H-lt
21
2
2
H-D
1
20
IB
4
N-D
1
9
11
2
H-D
H-D
12
L 10
B400
29200
91000
2140
4IB
24700
1310
17100
IBO
14700
7
10000
N-B
N-B
l»0
N-B
90
N-0
41
H-D
H-B
H-D
270
H-D
H-B
H-B
290
H-D
1200
H-D
H-D
70
N-D
H-D
220
120
74
N-D
N-D
N-D
H-D
H-D
BO
L 19
410
2300
1MO
4100
130
ISO
4940
1040
2940
200
2740
14
2700
H-D
H-D
9
20
14
H-D
10
N-D
It
26
13
H-D
H-
N-
H-
H-
12
N-
H-
N-
M-
H-
N-
H-
N-
H-
H-
H-
H-
H-D
H-D
L 10
74
POLLUTANTS Mill LISTED UtftE NOT DETECTED AT ANY BAHPLE POINT ON B1/02/23
L-LES8 THAN* G'GftEAIEK TKANI I-TR«CE» I OR J*INTERFERENCE» U-UNCONFIRHEDI
N-I'-HOI DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE liATE CND1NO BI/02/25 0800 HOURS
O
Ui
U>
FRACTION PARAMETER
HETAL3 BERYLLIUM
LAUMIUH
CHKUHIUH
COPPER
CYANII'C
LEAH
MERCURY
NICKEL
SILVER
ZINC
NOM-COMV. METALS ALUMINUM
0ARIUH
• OftOH
CALCIUM
COHALT
IRON
HAONCBIUH
HANOANESE
MOLYBDENUM
SODIUN
TITANIUM
VANAPIUH
YTTRIUM
UNITS
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L L
UO/L
UO/L
UO/L
INFLUENT
1
7
110
too
79
SO
300
st
4
370
L
L
L
L
8ECON0ARV
EFFLUENT
1
9
2V
2V
34
90
JOO
3f
1
leo
PERCENT
REMOVAL
L
29
74
71
99
-
-
-
ei
91
PRIMARY
EFFLUENT
1
4
120
»2
«4
44
400
81
4
340
PRIMARY
8LUDOE
17
80
4400
1400
1400
*40 L
30000 L
470
ISO
7100
SECONPARV
SLUDOE
2
30
1400
190
lf»
20
4000
SBO
IV
310
UO/L 3840
UO/L 110
UO/L 190
MO/L 92
UO/L 24
UO/L 2120
MO/L V
UO/L 2fO
UO/L 21
HO/L 243
UO/L 23
UO/L 4
UO/L L 9
940
34
V4
91
21
930
8
240
IV
304
L 3
L 9
L 9
89
47
34
2
13
79
II
17
10
78
17
3400
130
170
94
27
2030
V
2VO
22
2V2
2V
4
9
NOI RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOI RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
PULIUTANIS NOT LISTEIi UEKE NOI liETECTED AT ANY SAMPLE POINT ON Bl/02/29
L-K58 IHANi O'CRCATEk (HANI I'TRACEI I OR ^INTERFERENCEI U-UNCONFIRHEDI
N Ii'NOT DEIECteii.
-------
BA1LY ANALYTICAL RESULTS
CMAITAMUDOA
SAMPLE PATE tNOIHO Bl/02/24 OBOO HOURS
FKACDOM
COMVIMTIONALS
PARAMETER
DUD
TOTAL SUSP
COP
OIL I OREASE
SOLIE'8
n
Ul
HUH-COHUtNl lOHALS IOTAL PHENOLS
fUTAl SOLI PS
TOTAL USB. SOLIDS
TOTAL VOLATILE SOL IPS
VOLATILE PISS. SOLIP8
TOTAL VOL. BUS. SOL I PS
AMMONIA MITROOEN
TUC
VUL AT ILL'S
DAUE-NEUTKALS
METALS
HCNZENE
lilt 2-TRICHLOROE THANE
CHLOROFORM
ETHYLHENZENE
HETH1TLENE CMLOKIDE
TETRACHLORQETHYLENE
IOLUEHE
TRICHLOROETHTLENE
ACIP EXfKACT 2.4>4-l
2-CHLOROPHENOL
2»4-PICHLOROPHENOL
2> 4-blM£THYLPHENOL
2-NITROPMENOL
PHENOL
ACENAPiiniENE
1'3-DICm.OROIiCMZENE
1«4-P1CHLOROBENZENE
NAPHTHALENE
PIB<2-ETHYLHEXYL> PHTHALAIE
PI-N-PUIYL PHTHALAIE
DIETHYI. PHIHALATE
ACENAPHIHYLENE
PMENANTWKENE
AREENIC
*ERYLL!UM
CADMIUM
CHROMIUM
COPPER
CYANIC*
LEAP
MENCURY
NICKEL
POLLUTANTS NOT IISTEU UERE NOT PETECTEO AT ANY SAMPLE POINT ON 81/02/24
L-IES8 THANI 0»GREAT£ft THAN* 1'TKACfl 1 OK J'lNTERFERENCE* U'UNCONFIRMEPI
M-l>"NOT UEICCTEK.
UNITS
HO/L
HO/L
HO/L
HO/L
00/L
HO/L
ttO/L
MO/t.
MO/L
MO/L
MO/L
HO/L
ua/L
00/L
UO/L
UO/L
UO/L
UO/L
00/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UU/L
UO/L
UO/L
UO/l
UO/L
UO/L
UO/L
NO/L
UO/L
INFLUENT
340
217
740
32
B7»
IZ»0
1070
2»1
142
I2f
21
223
11
N-B
83
21
21
32
120
46
N-P
N-P
N-P
N-P
N-P
190
a
91
«
13
N-P
14
12
7
N-P
N-P
L 10
L 1
L 3
70
83
79
44
400
04
SECONDARY
CFFLUCHT
1 0
109
220
L 2
123
1140
1030
223
148
33
11
141
4
N-P
28
4
24
3
22
11
1
1
2
14
3
48
N-P
48
N-P
8
N-R
N-8
N-P
7
2
N-0
L 10
L 1
L 3
44
42
11
L 30
L 100
40
PERCENT
REMOVAL
m
30
70
»4
04
12
4
21
-
3?
11
28
44
-
47
• 1
-
VI
•2
77
-
-
•
-
.
44
»»*
47
»»»
47
-
m
»»t
-
-
-
.
-
-
47
4»
3?
22
30
29
PRIMARY
cmutMT
I 0
34
330
23
1000
»44
toa
42
14
24
14
to
12
N-P
»4
20
30
43
140
48
N-
N-
N-
N-
N-
N-
N-P
27
2
3
N-0
H-0
N-P
8
N-0
N-P
L 10
L 1
L 8
22
14
41
L 30
L 300
42
PRIMARY
ILUCOf
1*000
17407
47000
2470
1790
1B»00
1470
11100
140
10800
11
11000
7
110
43
33
13
200
230
140
N-0
N-D
N-0
N-P
N-B
N-D
N-P
1200
N-D
72
270
180
N-D
M-P
N-D
110
110
89
300
17000
IVOOO
1240
3800
10000
II 000
SECONDARY
SLUDOC
4400
3240
7400
181
223
4170
tio
1*00
140
1740
14
10000
M-0
N-P
23
f
*-D
10
14
N-P
N-D
N-D
N-0
N-D
N-D
N-D
N-D
72
N-D
N-D
N-D
N-D
N-D
H-D
M-D
N-D
110
10
00
itoo
BIO
223
440
L 4000
470
-------
DAILY ANALYTICAL RESULTS
CMAITANOOOA
SAMPLE DATE ENDING 84/02/24 0800 HOURS
FRACTION
HEIALS
NON-CONV. METALS
n
Oi
Ul
PARAMETER
SILVER
ttMC
ALUMINUM
DAR1UH
DORON
CALCIUM
COBALT
IRON
MAGNESIUM
HAHOAHESE
HOLYSPEMUN
SODIUM
TITANIUM
VANADIUM
UNITS
UO/L
UO/L
INFLUENT
8
280
SECONDARY
EFFLUENT
S
200
PERCENT
REMOVAL
10
39
PRIMART
EFFLUENT
1
120
PRIMARY
SLUOOC
4»0
toooo
SECONDARY
SLUDOE
190
3800
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
UO/L
HO/I
U8/L
UO/L
9300
140
140
91
II
3120
»
100
13
330
29
f
2810
82
110
SI
M
1340
»
240
13
28f
IB
L 3
41
91
13
13
12
28
44
420
31
100
4?
I*
480
8
220
L 10
270
L 9
L 9
HOT RUN
HOT RUH
HOT RUN
HOT RUN
NOT RUH
NOT RUM
HOT RUN
HOT RUN
HOI RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUH
HOT RUH
NOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LISTED HIRE NOT DETECTED AT ANY SAMF'LE FOIMT ON 8I/O2/24
L-LC3S THAN* 0-OREATER THAN* T-TRACEI I OR J*INTEftFERENCE» U>UNCONFIRHED»
N 11'NOT HETECTfD.
-------
DAILY ANALYTICAL RESULTS
CHAITAMOOOA
SAMPLE DATE EMMNU 81/02/27 0800 HOURS
K, AC II ON
COHVEHfIOMAL8
PARAMETER
»0tl
TOTAL SUSP.
COD
OIL I OREA8E
BOLIDS
o
Ul
NON-COMVENTIONAL8 TUTAL PHENOLS
TOTAL BOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIS8. SOLIDS
TOTAL VOL. SUS. SOLIDS
AHHONIA NITROOEH
TOC
VOL A III EB I'ENZENE
CHLURODENZENE
lild-TRICHLOROETHANE
I»I-DICHIOROETHANE
lil>2-TRICHLOROETHANE
I>112 > 2-TETRACHLOROE THANE
CHLOROFORN
Ii 2-TRANS-DICHLOROETHYLENE
li3-l>ICIILOROPROPYLENE
EIIIYLDENZENE
HEIHYLENE CHLORIDE
CHLORODIKROHOHETHANE
TETRACHLOROETHYLEHE
TOLUENE
IRICHLOROETHYLENE
2>4r4-|RICHLOROPHENOL
2>4-OICIUOROPHENOL
2.4-DIMETHYLPHENOL
PHENOL
HEUIKALS ACKNAPIIIHENE
I>2.4-TKICNIOROIIENZENE
Ii2-DICHLORO»ENZtNE
I.3-MCHIORO»ENZEHE
l.4-mCIILORO»ENZEME
FLUURANTIIENE
NAPHTHALENE
fcl8(2-ETIIYLHEXYL> PHIHALATE
DUTYI. BENZYL PHTHALAIE
DI-N-VUTYL PHTHALATE
DI-N-OCTYL PHTHALATE
PIETHYL PHTHALAIE
1.2-BENZAHIHRACENE
ANTHRACENE
FLUORENE
COLIUIAMI8 HOI LlSIEd WEhE NOT I'ETECIED AT ANY SAMPLE POINT ON 61/02/27
L-IES3 III AN I 0-OREAIER THAN* T-TRACEI I OR J-INTERFERENCE I U-UNCONFtRNEDI
H It-NOT DEIECTEH.
ACII'
UNITS
no/L
HO/L
no/L
MO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/t
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUEN1
410
236
010
41
BOO
1420
IUO
4«»
28*
IB1
l«
KB
U
B
II
1
2
9
ISO
J
1
2»
43
1
40
2«0
17
N-D
N-D
N-D
B*
N-D
92
M-0
4
l»
II
N-D
N-D
M-D
47
N-D
10
9*
t
4
8ECONDA
r EFFLUEN
74
SO
710
9
113
IMC
J0»0
317
2fB
J»
10
te
i
N-D
1
M-
M-
N-
4i
H-
»-
4
73
H-D
2
39
1
1
3
N-D
*
41
14
N-D
9
N-D
N-D
M-D
B
N-|>
t
N-D
37
N-D
N-D
N-D
RY PERCEN
T REHOVAI
62
81
74
68
61
20
I
26
.
7t
36
73
61
W
•1
W
ft*
?»»
*•
»»»
•*«
64
-
>»«
»3
67
»4
_
-
-
»J
.
73
-
-
»»»
»»»
-
-
-
91
-
-
»»«
»»»
»»«
F PRIMARY
EFFLUEN
440
21*
740
10
«70
1470
1230
444
320
144
14
2fO
12
N-D
33
N-
N-
H-
11
N-
N-
23
77
N-D
23
170
43
2
4
17
120
H-D
44
N-D
2
17
0
N-D
33
N-D
11
4
4»
N-D
4
9
PRIMARY
r SLUDOE
6100
12700
43000
3490
1400
14300
1930
6180
420
7740
37
10000
14
N-D
N-D
N-P
30
N-B
100
N-D
N-D
94
N-D
N-D
90
390
49
N-D
H-D
N-B
400
94
1800
140
N-D
64
130
940
14000
94
N-D
N-D
H-D
M-D
34
40
SE<
iLI
3H
44<
104
91
24
74'
10:
so
1*4
48
17
204
N-
N-
N-
H-
N-
N-
2*
N-
N-
10
H-
H-
7
90
M-
H-
H-
N-
H-
N-
23
H-
N-
N-
H-
80
N-
N-
N-
N-
H-
N-
N-
H-
CONDARY
IDOC
)0
to
)00
1
1
10
10
10
>
to
>0
-------
DAILY ANALYTICAL RESULTS
CHAITANOOOA
SAMPLE HATE ENDIHO 81/02/27 0100 HOURS
FRACTION
BASE-NEUTRALS
METALS
O
NON-CONY. METALS
PARAMETER
PHENAHIHRENE
PYRENC
ARSENIC
HERYLLIUM
CADMIUM
CMRDHIUH
COPPER
CTANIDE
LEAD
HEkCURV
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
IORON
CALCIUM
COSALT
IRON
MAGNESIUM
MANGANESE
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L L
UO/L
UO/L L
UO/L
UO/L
UO/L
UO/L L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
HO/I
UO/L
UO/L L
MO/L
UO/L
UO/L
UO/L
INFLUENT
4
f
10
2
9
180
as
43
90
400
84
1
240
4410
140
170
90
13
2140
»
270
10
303
28
9
42
SECONDARY
EFFLUENT
N-D
N-D
L 10
1 I
L 9
IT
L 10
•3
L 90
L 300
47
1
to
4*0
32
120
47
18
940
*
200
10
314
L S
t 9
L S
PERCENT
REMOVAL
»f»
W
I
90 L
-
89
et
-
t
29
22
84
42
72
77
2t
4
-
77
•
24
-
-
82
-
t»
PRIMARY
EFFLUENT
4
8
10
1
9
130
60
49
90
400
74
4
290
8840
130
140
93
19
2930
10
390
12
347
30
7
31
PRIMARY
8LUDOE
130
120
910
42
110
4400
3S«0
1080
2tOO
31000 L
1800
4 tO
13000
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
8LUDOE
N-P
N-D
490
12
00
3 tOO
1200
321
7tO
8000
7tO
230
4000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS HOI LISItll HERE NOT DETECTED AT ANY SAMPLE POINT ON 01/02/27
L-I.ES8 THANI O'ORCATER THANt T-TRACEI I OR J-INTERFERENCEI U-UNCONFIRHEDI
N-P-NOI PETECTEO.
-------
DAILY ANALYTICAL DCBOLTI
CHAITANOOOA
•AMPLE DATE ENPINO 81/02/28 0000 HOURS
FRACT I ON
CONVCHIIOHALS
PARAMETER
HOD
TOTAL BU8P. SOLID*
COD
OIL I ORCABE
NON-CONVENTIONALB IOTAL PHCHOL8
TOIAL SOLID*
TOTAL PI88. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISB. SOLIDS
TOTAL VOL. 8US. SOLIDS
AHHOHIA NITROOEN
TOC
Ul
00
VOLATILCB
ACII> EXTRACT
•ASE-NEUTRALS
NETAI-B
fcENZENE
i • i f I-IRICHLOROCTHANE
IiI>2-TRICHLOROETHANE
CHLOROFORM
1>2-TRANS-DICHLOROETHYLENE
EIIIYLBENZEHE
HETHYLCNE CHLORIDE
TETRACHLOROETHVLENE
TOIUENE
TRICIILORQETHYLENE
2>4fA-TRICHLOROPHEHOL
2>4-lilHETHYLPHENOL
PHENOL
ACENAPIIIHCNE
I•2,4-TRICHLOROIEHZEHE
It2-DICHLORO*ENZEHE
lf3-PICHLORO»CNZENE
1>4-PICHLORO»EHZEHE
li2-PIPHENYLHYPRAZINE
FLUORANTHENE
NAPHTHALENE
Dltt<2-ETHYLHEXYL> PHTHALATE
DI-N-»UTYL PHTHALATE
M-H-OCIVL PHTHALAIE
P1ETHYL PHTHALATE
DIMETHYL PHTHALATE
CHRYSL'NE
ANTHRACENE
FLUURENE
PHENANTHKENE
PYfcENE
ANTIHONY
AKtiEHlC
UNIT!
NO/L
HO/L
NO/L
HO/L
UO/l
no/i
NO/L
NO/L
NO/L
HO/L
HO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
270
270
4fO
23
750
1220
f44
3f4
21B
191
If
243
10
4
H-D
va
4
34
3400
IS
290
B
H-D
IB
110
N-D
37
H-D
B
19
N-0
1
N-P
36
f
7
IV
17
2
9
12
3
7
12
11
SECONDARY
EFFLUENT
7
48
140
9
110
1420
1970
449
40B
37
II
71
3
1
N-P
94
N-P
H-D
4B
2
30
N-D
1
B
f
1
13
N-P
2
11
N-D
N-»
H-»
3
If
N-P
14
13
N-P
N-P
1
H-B
N-P
L 9
L 10
PERCENT
REMOVAL
f7
•2
77
7B
Bl
-
-
-
-
77
42
7»
70
Bl
-
42
fft
fft
ff
f4
BO
fft
_
34
f2
.
74
-
73
4f
-
fft
-
•4
-
fft
24
24
fft
ff*
f2
fft
fft
SB
23
PMIHAIIY
EFFLUENT
240
142
970
14
700
1140
f74
311
2IB
fS
21
219
II
7
N-P
01
N-P
39
190
11
220
f
N-P
N-0
210
110
If
H-P
7
32
1
4
H-P
24
19
H-P
22
22
H-P
9
9
3
3
f
L 10
PRIHARY
BLUBOE
4200
1030O
3BOOO
3f40
1400
32000
1430
IBOOO
370
17400
37
7200
4
N-B
19
f3
H-B
40
21
79
430
If
N-D
N-D
310
N-P
B40
170
N-B
H-D
H-D
130
330
4BOO
N-D
140
N-D
N-D
N-D
N-D
N-D
f2
110
30
1100
BECOHDARV
BLUDOE
1300
B200
12000
433
230
f270
lOfO
4440
240
4300
17
2100
N-D
N-B
N-D
23
N-D
7
N-D
N-D
40
H-D
N-D
N-D
N-D
N-D
130
N-D
N-0
N-D
N-D
N-D
B4
3400
N-D
N-D
N-0
N-D
N-D
N-D
N-D
N-D
N-D
L 30
220
PULLUTANIS NOT I1SUU WERE NOT I'ETECTEP AT ANY SANPLE POINT OH BI/02/2B
L-LESS THAN) O'CREAIER THAN* t-TRACE! I OR J-lNTCRFERENCEl U-UNCONFIRHEDI
N-P-NOI HETCCTEP.
-------
6A1LY ANALYTICAL RE9ULIB
CHATIAHOOOA
SAMPLE DATE EHDIHO 81/02/18 0800 HOURS
FRACTION PARAMETER
n
METALS BERYLLIUM
CAIiNIUH
CHROMIUM
COPPER
CYANIDE
IEAP
MERCURY
NICKEL
SILVER
ZINC
NON-CONV. METALS ALUNINUN
MRIUH
•OKON
CALCIUM
COBALT
IRON
MAGNESIUM
MANGANESE
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L I
UO/L L
UO/L
UO/L
UO/L
UB/L L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
MO/L
UO/L
MO/L
UO/L
UO/L
UO/L L
INFLUCMI
1
S
4 JO
fl
30*
90
900
At
t
320
»330
ISO
170
40
10
3*70
9
330
243
37
7
9
SECONDARY
EFFLUENT
L 1
L 9
21
13
403
97
L 300
41
1
76
400
24
9t
49
II
440
a
1*0
2f3
L 9
L 9
L 9
PERCENT
REMOVAL
..
.
fS
at
-
-
40
•
03
74
*4
•4
44
*
3*
at
11
42
-
at
2»
-
PRIMARY
EFFLUENT
L 1
L 9
340
49
20*0
40
L 300
41
7
220
9740
»7
190
90
10
2190
t
200
27*
32
9
II
PRIMARY
BLUPOE
24
to
7000
3200
1220
2400
24000
1700
440
13000
NOT HUN
NOT RUM
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
SECONDARY
BLUDOC
7
40
3700
**0
234
930
L 4000
740
1*0
3«00
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
failUTAJHS NO I LISTED MEfcE NOI t'EIECTED AT ANY SAMPLE POINT ON 81/02/28
I **-'<:$'. THAN! G-GftfAItR IMAM) T-TRACEI I OR J-INTERFERENCE! U-UNCONF1RMEDI
P-9-WO! t-EIICT£!'.
-------
I'AILY ANALYTICAL kESULTS
CHAIIANUOOA
BAHfLE PA1E tMHINO MI/OJ/01 0800 HOURS
I MAC 11 ON
PAKAHEILR
CONtftNIIONAI
101 AL SUSP
COP
OIL I (IKE AGE
SOLIDS
NUN-CUNVEN1IONAL8 IOTAL PHEMULS
IUIAL SOLIDS
10IAL III 86. SOL I US
IOIAL VOIATUE SOL IDS
VOLATILE PIES. SOL IPS
101AL VOL. SUS. 801 IDS
AHHONIA NIIROOEN
IUL
VULAIILtS
cr>
o
AC IP EXTKACT
BASE-NEUIKALS
DiNIENE
CNLUROBEN/ENE
iltl-TRICHLOKOEIHANE
,1>2-1RICHLOROEIHANE
Ml OROFOKII
.I~DICIILOKOETHYLENE
.2-TRANS-PICIILOMOETMYLENE
>2-DICtlLOROPROPANE
ETH>L*ENIENE
HCTHYLEHE CHLORIPE
NEIMYL CHLORIDE
TEIRACHLOROEIHYLENE
IOLUENE
TRIUHLOROEIHYIENE
VINYL CHLOKII'E
2r4--DICHLOf(OPHEHOL
3>4-DINETIIYLfNENOL
PHENOL
ACENAPHIIIENE
l>2>4-fMICHLOROBENZeNE
l.l-DICIILOROPENZENE
1.4-MCHLOKODEN2ENE
tf2-DIPMENYLIIY[iftAZINE
FLUUkAMTMENE
NAPII1MAI ENE
N - NI IROaOtil -N-PROPYLAHIHE
Vlb<2 EIIIYLHEXYL) PN1HALATE
DI-N KUIYL PHTHALAIE
HIETIItL MIIHALATE
CIIRYSENE
ANIHRAL-ENE
KLUUKENE
PHEIIAMIHRENE
PYKENE
UNITS
HO/L
HO/L
HO/L
HO/L
UO/L
no/I
HO/L
HO/I.
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UG/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
410
344
410
II
*IO
1110
1010
414
202
212
23
240
12
N-B
4
N-D
M-P
*0
N-D
1
M-U
12
350
ia
240
140
N-D
7
7
N-D
N-D
20
1
12
2
12
N-D
2B
4*
29
21
4
4
9
4
11
SECONDARY
EFFLUENT
14
23
120
V
120
»?5
»90
111
114
IV
14
92
2
N-B
N-D
H-»
22
N-B
N-D
N-0
4
41
N-D
N-D
29
2
N-D
N-B
12
N-D
N-D
2?
11
N-P
N-0
N-P
N-D
N-D
•
N-D
17
N-P
N-P
1
N-0
N-P
PERCENT
REMOVAL
91
ffl
ai
11
• 7
28
4
AI
44
91
44
78
ai
-
tft
-
-
»»»
-
»f»
-
-
tft
m
»o
¥»
-
»»l
-
-
.
-
-
»»»
«»l
»»t
-
»»t
81
»»»
ir
»»t
m
80
»»»
»»»
PNINAMT
EFFLUENT
140
210
970
43
1190
mo
*3»
2V4
178
lit
2*
210
13
2
4
4
74
N-D
1
N-D
24
140
N-D
24
270
to
10
3
N-P
280
N-D
12
I
7
N-D
3
N-D
9
2*
A
»
N-D
2
2
2
1
MIHAftr
SLUBOE
1000
28100
24000
1340
1730
2*800
1310
13BOO
180
13400
42
uoo
N-D
H-D
N-D
80
44
N-0
H-D
N-P
30
32
N-D
48
440
«3
N-D
N-D
N-D
N-D
94
440
N-D
N-
N-
12
12
N-
N-
N-
H-
N-
N-
N-0
73
84
SECONDARY
SLUDOE
3100
11100
11000
143
223
12100
810
rsoo
140
»340
14
700
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-P
120
N-D
N-P
N-P
N-P
40
N-P
H-P
N-D
N-D
N-D
N-P
N-P
N-P
N-P
POLLUIANlb NOT IIBIEU WCkE NOT DEIECTED AT ANY SAHPLE POINT ON 81/01/01
L-LESS III AN I Q'OREAIEM 111 AM I T-TkACEl I OR ^INTERFERENCE! U«UNCONFIRHEDI
N D-NOI i-cueun.
-------
DAILY ANALYTICAL RCBULTB
CHAUANOOBA
SAMPLE DATE EMPINS •1/01/01 0100 HOURI
FRACTION PARAMETER
HEIAt8 ANTINOMY
ARBENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
ZINC
MON-COMVi NETAL9 ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
MAONEBIUH
HANOANEBE
MOLYBPENUN
BOPIUN
TITANIUH
VANADIUM
YTTRIUM
UNITB
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
MO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
L
L
L
L
L
L
L
INFLUENT
B
14
1
9
41
57
33
41
300
90
10
4
200
17000
130
140
93
12
4280
to
BOO
10
2t3
99
V
9
L
L
L
L
L
L
L
L
L
L
L
L
BCCONBARY
CFFLUENT
9
10
1
s
10
44
170
90
)00
90
10
1
97
290
21
130
49
13
3VO
•
220
12
247
9
9
9
PERCENT
REMOVAL
_
2f
-
-
7V
It
-
IB
-
-
-
79
71
VV
•4
7
19
-
VI
20
94
*
f
VI
44
-
L
L
L
L
L
L
L
L
PRIMARY
EFFLUENT
9
10
1
9
43
120
39
90
300
90
10
4
140
BV40
V4
94
47
14
2430
V
340
10
271
4t
7
7
PRIMARY
BLUDOE
310
1900
40
140
IVOOO
7100
1020
4200
22000
2900
BO
710
23000
NOT R|IM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
BLUBOE
•0
100
13
70
330*
1100
210
470
L 400*
BIO
L 30
210
330*
NOT RUN
NOT RUN
NOT RUN
NOT RUM
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS HO! LISTED WERE NOT PETECTEH AT ANY BAIIPLE POINT ON Bl/03/01
L-LC88 TMANI 0-OREATER THAN I T-TRACEI I OR J'INTERFEREMCEl UMINCOHFIRHEBI
N-D>MOT DETECTED.
-------
BART ANALYTICAL RESULTS
CHATIAHOOOA
SAMPLE DATC CNl'INO 81/03/02 0(00 HOURS
FRACTION
CONVENTIONALB
PARAMETER
DOO
TOTAL SUSP. SOLIDS
COD
OIL I ORCASE
NON-CONVENT IONALS TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DI8S, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE 0188. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHNONIA NITROGEN
TOC
VOLATILES BENZENE
CHLOROBENZENE
111 • 1 - TRICHLOROE T HAHE
CHLOROFORM
ETHYLBENZENE
HETHVLENE CHLORIDE
TETRACHLOROETHVLCNE
TOLUENE
TRICHLOROETHYLENE
2i 4-DICHLOROPHEHOL
PHENOL
ACEHAPHIHENE
I r 2i 4,-TRICHLOROIENZEHE
!»2-DICHLORO»ENZENE
Ii3-DICHLOROBENZEHE
I•4-DICHLOROBCHZEHC
FLUORANTHENE
HAPHTHALENE
DIS<2-ETHVLHE»VL> PHTHALATE
BUTYL BENZYL PHTHALATE
DI-N-BUTYL PHTHALATE
METHYL PHTHALATE
I>2-BENZANTHRACENE
CKRYfiENE
ANTHRACENE
FLUORENE
PHEHANIHRENE
PYREHE
METALS ANTIMONY
ARSENIC
BERYLLIUM
CADHIUM
CHROMIUM
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON 81/03/02
L-LES8 THAN* O'OREATER IHANI T-TRACEI I OR J-1NTERFERENCEI U-UNCOHF1RHEDI
N-D-HOr DETECTED.
ACID EXTRACT
BASE-NEUTRALS
UNITS
HO/I
HO/L
HO/I
HO/t
UO/L
HO/L
HO/L
HO/L
NO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L L
UO/L L
UO/l L
UO/L
INFLUENT
IfO
122
430
10
fSO
io»o
f4B
20*
12*
•1
33
170
12
2
24
14
12
120
It
310
12
2
200
N-D
S
M-0
]
N-P
2
N-0
3
N-D
2
2
N-D
N-0
1
1
1
2
9
10
1
3
43
SECONDARY
EFFLUENT
17
23
83
2
43
f33
f!2
04
70
H
U
3d
2
N-D
H-»
17
N-D
• 4
N-D
4
N-0
H-»
f
1
•
N-D
1
H-D
N-D
N-D
3
N-D
N-D
2
N-D
N-D
N-D
1
N-D
N-D
L 9
L 10
L 1
L 3
L 10
PERCENT
REMOVAL
91
• 1
ai
Of
fS
14
4
40
44
03
32
7f
03
ff*
W
f»»
30
m
99
W
99 i
97
_
-
-
47
-
m
-
40
-
99 1
-
-
-
99t
-
99 1
m
I
i.
I
L
77
PRIMARY
EFFLUENT
230
211
330
13
•70
1200
ff4
242
120
122
29
210
II
N-D
14
70
29
110
17
290
IB
N-D
470
N-D
4
N-D
1
1
N-D
N-D
4
N-0
N-D
2
N-D
N-D
N-D
N-D
N-D
N-D
3
10
1
3
31
FRINARV
BLUDQE
3300
2D200
34000
2700
2400
2MOO
1240
17000
340
14400
40
2100
H-D
N-D
N-D
43
30
73
N-D
420
•0
N-D
270
N-D
040
ISO
N-D
12
230
400
430
140
N-D
N-D
• t
03
120
04
210
IfO
1»0
1100
110
240
24000
SECONDARY
SLUOOE
If 00
7320
0200
210
14?
0310
?»0
4040
140
3fOO
17
320
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
BO
N-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
N-D
L 40
73
7
.30
3400
-------
DAILY ANALYTICAL RESULTS
CHATTAHOOOA
SAMPLE DATE ENDINO BI/03/02 0800 HOURS
FRACTION PARAMETER
n
o>
U>
METALS COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
NON-CONV. METALS ALUMINUM
•ARIUH
•OfcOM
CALCIUH
C0«ALT
IRON
MAGNESIUM
HAHOAHEBE
SODIUM
TITANIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
MO/L
UO/L
UO/L
INFLUENT
92
23
L 90
300
71
2
110
24fO
72
3f
49
7
1B40
9
310
274
11
L 9
SECONDARY
EFFLUENT
11
47
L 30
L 300
L SO
L 1
38
240
IV
70
41
10
200
f
220
2*7
L 9
L 9
PERCENT
REMOVAL
73
-
L
L
30
SO
AS
»1
74
-
4
-
BV
-
2»
-
«2
-
PRIMARY
EFFLUENT
34
21
30
300
to
3
140
71BO
»4
34
44
10
2400
»
180
270
23
f
PRIMARY
SLUDOE
14000
843
fOOO
23 L
7300
1200
4VOOO
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOI RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
SECONDARY
SLUDOE
1100
7?
400
4000
730
230
3000
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LISTED MERE NOT DETECTED AT ANY SAMPLE POINT OH BI/03/02
L-LES9 THAN) O'OREATCR THAN! T-TRACEI I OR J-INTERFERENCE* U-UNCONFIRMEOI
H-D-NOI DETECTED.
-------
PAILV ANALYTICAL RESULTS
CHATTANOOBA
ADDITIONAL SAHPLE POINTS
BANPLE PATE ENDING 01/03/02 0800 HOUK8
FRACTION
CONVENT IONALB
PARAMETER
•01
TOTAL BUSP
COO
OIL I CREASE
BOLIPB
o\
ACIP EXTRACT
•ABE-NEUTRALS
NON-CONVENT IONALS TOTAL PHENOLS
TOTAL SOLIbS
TOTAL PISS. 80LIPB
TOTAL VOLATILE SOLIP8
VOLATILE PIBS, SOLIPS
TOTAL VOL. SUB. SOL IPS
AHHONIA NITROOEH
TOC
VOLATILES PCNZENE
CHLOROIEN1ENE
liltl-TRICHLOROETHANE
CHLOROFORM
I>2-TRAN8-OICHLONOETHYLCNE
ETHYLPEHZENC
NETHYLtHE CIILORIPE
TOLUENE
2>4-IIIMETHTLPHENOL
PHENOL
||2>4-TR1CHLORO*ENZENE
li]-OICHLOROI>ENZENE
I«4-PICHLORO»EN2ENC
li2-OIPHENYLHYPRAZINE
FLUORAHTHCNE
»I8I2-CHI.OROETHYOXY> NETHANC
PIS(2-CTHYLHCXYLI PHTHALATE
PI-N-PUTYL PHTHALATE
PI-N-OCTYL PHIHALATE
PIETHYL PHIHALATE
CIIRYBENE
ANTHRACENE
FLUORENE
PHENANTHDENE
PYRENE
NETALB ARSENIC
CAOHIUN
CHROHIUn
COPPER
CYANIVE
LEAD
MERCURY
POLLUTANTS NOT LIBIEP HERE NOT PETECTEP AT ANY BAHPLE POINT ON 01/03/02
LM.EB8 THANI O'OREATER THAN* T-TRACEI I OR J'INIERFERENCEl U-UNCONFIRHEOI
N-P-NOI PETECTEP.
UNITS
HO/L
NO/L
HO/L
HO/L
UO/L
MO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UQ/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
VACUUM FILTER »IOESTER IAP
FILTRATE SUPERNATANT HATER
• 1
101
4*0
n
240
17*0
1)10
at
HO
fl
100
200
a
N-
N-
N-
N-
N-
M
14
IB
4
H-P
7
1
N-P
4
9
44
a
14
10
2
S
t
9
4
1*
L 9
110
110
3*
02
000
110
«»4
1100
14
400
3200
isto
71*
124
its
100
119
12
90
1
1
22
100
U
190
M-P
29
A
II
4
9
4
H-P
19
4
14
II
2
N-0
*
N-0
4
10
9
110
220
44
140
1*00
I 1
2
L 29
L 2
t 9
I2«
124
14
12
2
L 1
4
2
1
1
10
N-0
N-D
4
4
N-
N-
N-
N-
M-
N-
N-
N-
T2
4
N-
N-
H-
H-
N-B
N-P
N-D
L 10
L 9
L 10
L 10
*
L 90
L 100
-------
DAILY ANALYTICAL RESULTS
CHATTANOOItA
ADDITIONAL SAMPLE POINTS
SAMPLE DATE ENDINO Bl/03/02 0800 HDUkfl
FRACTION
HCTALS
PARAMETER
NICKEL
SILVER
ZINC
UNITS
VACUUM FILTER
FILTRATE
•IBESTER
SUPERNATANT
TAP
HATER
l/l
NON-CONV. METALS ALUMINUM
SAR1UH
•DRON
CALCIUM
COBALT
IRON
MAOHESIUH
HANOANE8E
MOLYDDENUN
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
NO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
74
9
400
7370
220
UO
24 i
II
4950
3*
2110
10
2«l
30
s
33
ISO
9
700
19000
340
240
240
29
10000
1»
2400
10
29*
90
10
T7
L 90
L I
37
9*
21
20
23
9
30
4
10
JO
79
9
9
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT ON 01/03/02
L-LESS THAN* 0-OREATER IMAHI T-ISftCEt I OR J-IHTCRFERENCEI U-UNCONFIRNEDI
N-ti-NOI DETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
BAHPLt PATE ENDIHO BI/03/03 OBOO HOURS
FRACTION
CONVENTIONAL!
PARANEIER
HOB
TOTAL SUSP
COD
OIL I ORCABE
SOLIOB
9
NON-CONVENT10NALS TOTAL PHENOLS
TOTAL BOLID8
TOTAL DI6B. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE 6188. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHNONIA MURDOCH
TOC
VCILAIILES BENZEHE
CIILOROBENIENE
1.1.I-TRICHLOKOETHANC
1•1.2-IRICHLOROETHAHE
CMLOROFORH
l>2-TKAN8-DICHLOROeTHYLCNE
ETHYLDEHIENE
HETHYLEHE CHLORIDE
TRICHLOROFLUOROKETHANE
TETRACHLOROETHTLENE
10LUEHE
IRICHLOROETHYLENE
21414-T RICHL OROPHEHOL
PAftACHLOROHETA CRE80L
2<4-DICHLOKOPHENOL
2f4-BINETHYLPIIENOL
PHENOL
ACENAPIITHENE
I>2»4-TRICHLORO»ENZENE
D1SI2-CHLOROETHYL> ETHER
lt3-DICIILOROBEHZCNE
l>4-DICHLOR08ENtENE
l>2-DIPHENYLHYIiRAZINE
FLUORANIHENE
HAPHTHAl ENE
BISC2-ETH¥LHEXYL» PHTHALATE
DI-N-BUrYL PHTHALATE
DI-H-OCTVL PHTHALATE
DIETHYL PHTHALATE
DIMETHYL PHTHALAIE
l.2-»fNZANTHRACENE
CHRYSENE
ANTHRACENE
FLUORENE
POLLUTANTS HOT LISTEP UEftE NOT liEIECTEP AT ANY B AMPLE POINT OH BI/03/03
L-LESS THAN! O'OfiEAIER UIAHI T-TRACEI I OR J'lHIERFERENCEl U-UHCOHFIRHEDI
AC1P EXTRACT
BASE-NEUTRALS
UNIT8
HO/L
HO/L
NO/L
HO/L
UO/l
HO/L
HO/L
NO/L
HO/L
NO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
U0/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
SECONDARY PERCENT PRIMARY PR IN ART
INFLUENT EFFLUENT REHOVAL EFFLUENT SLUOOE
450
21*
BIO
19
900
12*0
1070
319
170
149
22
203
•
N-D
10
N-B
no
N-B
17
120
4
34
230
13
N-D
N-D
3
N-D
270
2
II
4
9
II
1
i
H-D
S
2
N-B
1
H-D
N-D
N-D
H-D
2
2*
29
240
1
9B
ffl>
*3B
IOB
fO
IB
U
47
1
H-D
N-D
2
40
H-D
t
fj
H-D
H-D
10 •
1
H-D
N-D
N-D
2
N-D
H-D
4
H-D
H-D
H-D
H-D
N-D
N-D
N-D
3
97
7
2B
H-D
H-D
H-D
H-D
»4
BB
4*
B4
BB
24
10
44
47
BB
27
04
BB
-
»»»
-
44
-
t4
22
*»*
W
• 4
»2
_
-
W
-
»*»
»»»
44
W
W
*»*
»»«
t»»
-
m
-
-
-
-
~
-
-
»»«
430
1*9
790
41
470
13*0
11*0
370
290
128
23
110
10
1
12
N-D
110
1
23
240
H-D
17
230
12
1
3
4
H-D
120
220
II
N-D
4
7
H-D
3
N-D
B
3
2
II
14
H-D
H-D
2
2
3400
17000
41000
34BO
1190
10200
1220
11000
ISO
10400
94
f90
H-D
H-D
24
BO
H-D
N-D
*0
N-D
N-D
4*
4BO
130
H-D
N-D
N-D
N-D
110
44
970
N-
H-
H-
N-
21
41
H-
N-
H-
N-
N-
9*
40
B4
40
UCONDARY
BLUDOE
2000
9790
4100
30*
143
4700
*90
4320
140
4IBO
24
440
N-
H-
N-
H-
30
N-
N-
N-
H-
N-
N-
N-
N-
N-
H-
H-
H-
N-
H-
N-
N-
N-
N-
N-
N-
H-
N-
N-
N-
N-
N-
N-
N-
N-
-------
DAILY ANALYTICAL RESULT!
CHAITANOOOA
SAMPLE DATE ENDING 81/03/03 0800 HOURS
FRACTION
BASE-NEUTRALS
METALS
n
cr>
NON-CONV. METALS
PARAMETER
PMENANTHRENE
PYREHE
ANTIMONY
ARSENIC
•ERVLLIUH
CADHIUH
CHROMIUM
COPPER
CYANIDE
LEAK
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
•OKOM
CALCIUM
COBALT
IRON
MAGNESIUM
MANGANESE
SODIUM
TITANIUM
YTTRIUM
SECONDARY PERCENT PRIMARY PRIMARY SECONDARY
UNITS INfLUENT EFFLUENT REMOVAL EFFLUENT SLUDOE SLUDGE
UO/L
UO/L
N-D
2
UO/L 17
UO/L L 10
UO/l 4
UO/L 40
UO/L 140
UO/L 78
UO/L 127
UO/L 74
NO/L 400
UO/L 34
UO/L 7
UO/L 110
UO/L 1330
UO/L ISO
UO/L 140
HO/L 32
UO/L 7
UO/L 2440
HO/L f
UO/L 300
HO/L 312
UO/L L 90
UO/L 10
M-D
N-D
L 10
L 10
L I
2»
IT
14
132
32
L 300
3?
I
33
310
24
48
43
10
?7
230
320
72
L 3
41
79
27
84
7»
30
23
84
83
fl
84
97
13
94
23
90
2
N-D
L 10
L 10
L I
28
94
90
183
30
400
41
7
230
4130
120
120
92
L 9
2310
10
330
318
L 90
13
ISO
170
130
3TO
100
230
17000
9800
930
9300
38000
4000
1200
30000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
N-D
N-D
40
93
IB
30
3400
1100
44
400
L 4000
720
200
3300
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS KOI II6TEK UEkE NOT DCIECTED AT ANY SAMPLE POINT ON 81/03/03
I 'LESS MIAN! 0-OKCAUK TIIANI T'TRACEI I OR J>INTERFERENCE I U»UNCOHFIRMEDI
N-ti-NIII IiEUCTEIi.
-------
DAILY ANALYTICAL RESULTS
CIIAIIANOOBA
BAMFLE DATE ENDINO HI/01/04 08OO HOURS
FRACIION PARAMETER
O
CO
CONVENTIONAL HOD
TOTAL SUSP. BOLIM8
COD
Oft I OREASE
NON-CONVENT IONALS TOTAL PHtMOLi
IOIAL BOLIIlS
lOIAL DIBS. gOLIPS
IOIAI VOLATILE SOLIDS
VOLATILE CII9. SOLIDS
IOIAL VOL. BUS. SOLIDS
AHflUNIA NITROGEN
IOC
VOL AIIICS
ACID EXTRACT
BASE-NEUTRALS
HEIALS
•EN2EME
CMLOROBENZENC
Itlil-TRICHLOROETHANE
CHLOROFORM
I.2-1RAN8-UICHLOROETHYLENE
flHYLBENZENE .
HETHVLENE CHLORIDE
TEIKACHLOROETHYLENE
TOLUENE
IRICIIIOROEIHYLENE
2>4-PIMETHYLPIIENOL
FIIENOL
ACtNAHIIIIENE ,
li2i4-IRICHLqROIiLNZEHE
li2-DICIILOROtiENZENE
It3-MCHLORO»ENZEHE
I•4-DICHLOROBENZENE
lt2-PIPHENYLHrDRAZINE
FLUOftAHTHENE
NAPHTHALENE
»IS(2-E!im.HEXU> PIITHALAIE
BI-N-fcUTYL PHTHALAIE
DI-N-OCIYL PtmiALATE
PUTHYL PHIHALATE
lt2-BEH2ANIHRACEME
CHRY8ENE
ANIMRACENE
FLUOKENE
PHENANIHRENE
INliENO(l>2>}-C>P> PYRENE
ANTINOMY
ARSENIC
BERYLLIUM
UHITB
MO/L
no/t
HC/L
HO/L
UO/L
MO/L
HO/L
MO/L
no/L
HO/L
no/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UD/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUEI
420
349
»00
11
420
1410
1240
J4I
130
211
20
139
II
N-l>
7
•4
N-B
29
144
IB
170
•
4
190
2
11
N-D
4
4
I
N-D
N-D
4
1
N-B
1
N-D
N-D
1
2
N-D
H-B
L 10
14
12
SECONDA
«T EFFLUEM
92
II
240
4
BO
MOB
1070
74
92
24
14
10
4
H-B
2
44
N-D
14
10
14
27
2
N-B
12
N-tl
4
N-D
1
2
N-B
N-D
N-D
4
1
N-D
1
H-B
H-B
N-D
1
H-B
N-D
L 10
L 10
L 1
ftY PERCE
T REHOV
••
f2
71
88
• 1
11
IS
7»
49
•9
30
74
44
-
71
47
-
44
71
SB
84
79
»»»
»2
»»<
4»
-
81
47
W
-
-
13
47
-
-
-
-
»»*
SO
-
-
_
29
92
UT PRIMARY
»L EFFLUEN
100
214
BOO
17
400
1410
1220
249
I4B
121
20
309
14
2
N-B
110
1
4B
91
41
210
II
12
210
N-0
II
N-D
4
4
1
1
N-D
a
2
1
2
N-D
2
1
2
1
N-B
L 10
14
1
PRIHAR
r ILUDOE
7700
19400
17000
2110
900
14*00
1900
10400
310
101 00
14
W
N-D
N-D
N-D
49
N-D
47
140
190
140
49
N-D
220
N-D
990
110
N-D
7B
N-0
200
490
N-D
N-D
N-D
N-D
08
97
44
H-D
140
190
130
140
29
r SE<
SLI
29
94
79<
421
17
41
9I<
40
l><
19<
IB
90<
«-
H-
H-
27
N-
N-
N-
H-
N-
H-
H-
N-
N-
87
N-
»-
N-
N-
N-
78
N-
N-
N-
H-
N-
N-
N-
N-l
N-l
N-l
L 40
90
19
CONDARY
JDOE
90
10
>0
t
1
10
)
ro
>
>o
>
i
1
i
POLLUTANTS NOT LISTED UtKE NOT PETECTEB AT ANY fiAHPLE POINT ON 81/03/04
L^LESS THAN I 0-OKEAIEM IHANI T-TRACEI I OR J-INTERFERENCE! U-UNCOMFIRftEDI
M-l'-NOT UETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENIUNO 81/03/04 OBOO HOURS
FRACTION PARAMETER
METALS CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
HERCURY
NICKEL
SILVER
ZINC
NDN-CONV. METALS ALUMINUM
»ARIUM
»ORON
CALCIUM
COBALT
IRON
HAONESIUN
MANOANE8E
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/t
INFLUENT
20
110
• I
22
• 7
300
170
1
400
L
L
L
SECONDARY
EFFLUENT
12
IS
10
VI
SO
100
70
1
A3
PERCENT
REMOVAL
40
at
oa
-
23
-
47
06
84
PR1HARY
EFFLUENT
19
110
61
73
L 90
L 300
180
8
210
PRIMARY
SLUOOE
130
10000
4400
1280
2800
96000 L
2200
920
19000
SECONDARY
SLUDOE
90
3700
1300
32
180
4000
790
300
3609
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/I
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
*890
180
140
4V
V
2810
to
2VO
If
390
L SO
12
230
910
22
»7
44
L 3
320
9
210
L 10
324
94
L 9
L 9
V9
88
31
10
44
8V
10
28
47
7
98
tB
7410
130
140
47
L 9
2290
10
280
14
393
L 40
7
42
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
POLLUTANTS NOT I1BTED HERE HOI DETECTED AT ANY SAMPLE POINT ON 81/03/04
L-LESS THANI 0-OREATER THAN) T-TRACEI I OR J-INTERFERENCE I U-UNCONF1RHEDI
N-H-NOT DETECTED.
-------
DAILY ANALYTICAL RtSULIB
CHATTANOOGA
•AMPLE PATE ENDINO 81/01/09 0100 HOUKI
FRACTION
CONVENTIONAL!
PAflAMEYER
too
TOTAL SUSP
COD
OIL I OREASE
SOL IPS
n
-»j
o
NON-CONVENTIONAL 8 TOTAL PHENOLS
fOIAL SOLIDS
TOTAL D18S. 8 OLIOS
TOTAL VOLATILE SOLIDS
VOLATILE DIS8. SOLIDS
TUTAL VOL, SU9. SOLIDS
AMMONIA NITROGEN
TOC
AGIO EXTRACT
tlASK -NEUTRALS
METALS
DENZENE
CHLOftOHENZENE
till I -TRICHLOROETHANE
CHLOROFORM
VOLAT1LEB
HETHYLCNE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICIILOROETHYLENE
2>4-DICHLOROPHENOL
2i4-DIHETHYLPHEHOL
PHENOL
1 1 2 r 4- TRICHLDROfrEHZENE
Ifl-DICHLORODENZEME
ti4-DICHLOftO>EHZENE
FLUORANTHENE
NAPHTHALENE
•IS(Z-MHYLMEXYL) PHTHALATE
OUTIrL BENZYL PHTHALATE
DI-M-»um PHTHALATE
DI-N-OCTYL PUTHALATE
PIETHYL PHTHAI.ATE
l<2-BEN2ANrHRACENE
1 1 1 I2-0ENZOFLUORANTHEHE
CHKYBENE
ANTHRACENE
FLUOfcENE
PHENANTHKENE
PYRENE
ANIInONY
ARSENIC
BERYLLIUM
CADIUUH
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT ON Bl/OJ/03
I -CESS TKANJ 0-OfteAIEK 111 AH I T-TRAC£I I OK J»INTERFCREHCC» U'UMCONFIRItEDI
N-D-NOI DETECTED.
UNITS
HO/L
HO/L
HO/L
no/i
UQ/L
HU/L
HO/L
HD/L
HO/L
HO/L
HO/L
HO /I.
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
I/O/L
UO/L
UO/L
UO/L
UO/L
00 /L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UQ/L
Ud/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NUT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
EFFLUENT
ai
39
210
4i
93
941
904
12*
104
20
1
79
4
N-D
a
42
IB
290
It
S2
1?
N-«
N-D
B20
1
1
H-D
N-D
N-D
3
H-K
N-D
1
14
N-»
H-D
N-D
N-»
H-D
N-D
N-D
L 10
L 10
L 1
9
PERCENT
REMOVAL
.
-
-
-
_
-
.
-
-
-
-
-
.
-
-
-
-
-
-
-
-
_
-
-
_
-
-
-
-
•
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
PRIMARY
EFFLUENT
110
>74
SBO
94
320
1020
842
2SI
192
99
9
200
14
2
24
7B
110
ISO
10
390
72
44
11
110
9
1
1
2
N-D
9
N-D
4
H-D
97
N-D
N-D
2
2
1
2
2
L 10
12
L 1
IB
PRIHARV
BLUDOC
2100
24400
11000
2S40
041
29900
1110
13200
130
moo
30
710
M-D
H-D
N-D
90
40
N-D
130
270
3>
N-D
N-D
N-D
910
N-D
N-D
220
940
N-D
140
N-D
N-D
H-D
74
92
74
to
7B
160
170
40
240
49
70
SECONDARY
SLUOOE
3700
7770
14000
494
IBS
B430
B40
9290
170
SI 20
21
390
H-
N-
H-
25
N-
N-
N-
99
N-D
N-D
N-D
N-D
90
N-D
N-D
44
B4
N-D
H-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
N~D
N-D
94
L 10
20
40
90
-------
DAILY ANALYTICAL RESULTS
CHATIANOOOA
SAMPLE PA IE EHDINB Bl/OJ/03 0800 HOURS
FRACTION
MEIALS
NON-CONV. NETALB
?
PARAMETER
CHROMIUM
COPPER
C VAN I [it
LEAD
HERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUN
BORON
CALCIUM
COVALf
IRON
NAONESIIIH
HANOANCBE
BODIUN
VANADIUN
YTTRIUM
UNITS
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
NO/L
UO/L
UO/L
INFLUENT
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
EFFLUENT
27
L 10
47
L SO
L 300
35
1
SB
410
21
41
3*
B
340
a
IBO
248
L 9
L 9
PERCENT
REMOVAL
_
-
-
-
-
-
-
-
.
-
-
-
-
-
-
-
-
-
-
PR I HART
EFFLUENT
200
41
117
94
30*
97
9
309
9970
120
79
44
14
3130
7
230
213
V
94
PRINART
8LUDOE
3700
2900
1090
3400
43000
1300
330
f400
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
SLUDGE
9100
1700
1*2
MOO
»ooo
930
390
9300
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
POLIUIANTS NOT 1I8TEK HE HE NOT OEUCTCD AT ANY SAMPLE POINT ON 81/03/09
L-IESS TNANI O-ORCATFR MIAN* T«IRACEI t OR J-INTERFERENCCI U'UNCOHFIfiHCDl
N-ti-MOr littECTH'.
-------
HAItr ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE PATE EMDINO 01/01/0* OBOO HOUR!
FRACTION
CONVENTIONALB
O
•vl
N)
PARAMETER
HOD
TOTAL SUSP. SOLIDS
COD
OIL I OREA8E
NON-CUNVENflONALS TOTAL PHENOLS
rOlAL SOLIUS
TOTAL PISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE Dl'SS. SOLIDS
TOTAL VOL..6US. SOLID9
ANHONIA NITROaCH
TOC
VOLAIUES tENZENE
CHLORODEHZENE
111. l-TRICItl OMOEIHANE
ltit2-IRICHLOftOEIHAN£
CHLUKOfORH
ETHYlkEHZCME
HETHTLENE CHLORIDE
TETRACHLOROCIHYLENE
TOLUENE
TRICItLOROLTHYlEME
2H-DICHLOROPHENOL
PHENOL
1.2»4-TRICHLOftODENZENE
1.1-DICM.OKOBENZEHE
I>4-DICHLORO>ENZENE
I>2-DIPIlENYLHYI'RAZINE
FLUORANTHENE
NAPHTHALENE
BI8(2-ET1IYLHEXYL) PHItlALATE
Pl-H-KUTYL PHTIlALATE
DUIMYL PHTHALAIE
ANTHRACENE
FLIIDRENE
FHtNANIHKENE
PYRENE
HETALS ANTINOMY
AhiiENIC
liLkYlt IIIH
CADH.IUH
CHROMIUM
COPPER
CYANIDE
LEAD
POLLUTANTS N01 LISTED UEftC HOT DETECTED AT ANY SAMPLE POINT ON 81/03/04
L-LESS THAN! 0-GRCAIEK THANt T-TRACEI I DM J-INTERFERENCE I U»UMCOHFIRftEDI
N-ll-NOT DETECTED.
ACID EXTRACT
KASE-NEUTRALB
UNITS
HO/L
NO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L .
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L L
UO/L
UO/L L
UO/L
UO/L
UG/L
UO/L
UO/L L
INFLUENT
410
347
870
U
420
13*0
1040
358
294
2*2
12
379
43
3
11
N-p
VI
18
47
33
1200
i
22
500
4
2
a
i
N-»
N-0
3
2
2
1
1
1
N-0
10
10
1
12
140
91
At
30
SECONDARY
EFFLUENT
3V
42
210
3
209
tie
at*
209
174
31
7
73
la
N-0
3
N-0
42
9
29
9
*70
1
17
47
4
2
3
N-D
N-
N-
N-
M-
9
N-
N-
N-
H-
L 10
L 10
L I
3
92
L 10
34
L 30
PERCENT
REMOVAL
a*
aa
7*
4T
47
33
14
41
41
8»
42
01
38
m
73
-
97
72
47
83
44
83
23
91
33
-
40
»»t
-
-
»t»
»»«
-
991
99 »
99 »
-
L
-
L
38
83
89
44
L
PRIHARY
EFFLUENT
280
274
740
22
«00
1300
1030
444
242
184
12
310
48
3
14
N-D
110
29
39
38
1900
7
17
490
3
N-D
N-
N-
N-
H-
N-
N-
4
H-
N-
N-
N-
10
10
1
12
320
47
33
30
PRIHARY
SLUPOE
2200
24700
17000
1420
400
23900
1200
19300
340
14900
23
830
38
N-D
N-D
82
77
74
N-P
N-D
1400
190
N-P
N-D
410
N-D
N-D
N-D
140
390
H-D
N-D
N-D
N-D
N-D
140
130
180
240
34
240
14000
7100
89*
4400
SECONDARY
ILUDOE
4000
8320
11000
493
288
9080
740
4300
130
4190
14
910
11
N-D
N-D
N-D
33
N-D
N-D
39
1300
N-D
H-D
N-P
74
N-D
N-P
N-D
42
aa
N-D
340
N-D
N-D
N-D
N-D
52
as
190
27
80
3900
1400
203
940
-------
BAILY ANALYTICAL RESULTS
CHATTANOOGA
BAHFLE DATE CMPINO 81/03/04 0600 HOURS
FRACTION
HEIAL8
NON-CONVf METALS
O
»-J
CO
PARAMETER
MERCURY
NICKEL
SILVER
tINC
ALUMINUM
IAR1UN
•OROH
CALCIUM
COfALT
IRON
HAONESIUN
HANOANEBE
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
NO/L
UO/L
oa/L
UO/L
INFLUENT
400
94
4
240
L
L
SECONDARY
EFFLUENT
900
90
1
It
PERCENT
REMOVAL
25
7
»
89
PRIMARY
EFFLUENT
400
40
9
240
PRIMARY
SLUPOE
61 000
4900
B30
27000
8ECOHUARY
SLUDOE
VOOO
700
230
4400
UO/L 4770 910 11 9*10 NOT RUN NOT RUN
UO/L 130 21 02 120 NOT RUM NOT RUN
UO/L 110 4V 37 120 NOT RUN HOI RUN
HO/I 39 44 14 94 HOT RUN NOT RUN
UO/L 90 IB 44 42 HOT RUN NOT RUN
UO/L 2B90 200 93 2440 NOT RUM NOT RUN
HO/L 1 B II f NOT RUN NOT RUN
UO/L 270 170 37 270 NOT RUN NOT RUN
UO/L 12 L 10 17 II NOT RUN HOT RUN
NO/L 273 249 10 244 NOT RUN NOT RUN
UO/L L 90 4f - L 90 NOT RUN NOT RUN
UO/L 4 L 9 17 • NOT RUN NOT RUN
UO/L t L 9 44 10 NOT RUN NOT RUN
POLLUTANTS NOT LISUH HERE NOI DETECTED AT ANY SAMPLE POINT ON 61/03/04
L-IES9 THAN! 0-OREATER TMANI T-TRrtCEl I OR J-INTERFERENCE I U-UNCONFIRMCDI
N I»NOT t'ETECTED.
-------
HAIL IT ANALYTICAL RESULTS
CIIATTAHDOOA
SAMPLE HATE END1NO 11/01/07 OBOO HOURS
FRACTION
CONVENTIONAL 9
PARAMETER
SOL I PS
O
TOTAL SUSP
COII
OIL I GREASE
NON-CONVCNTIONALtt TOTAL PHENOLS
TOTAL SQL I US
TOTAL Dttt. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHHOHIA NITROOEN
TOC
VOIAT1LCS fiENZENE
CHLOROBENtENE
li2-DlCm.OROETHAME
I l I . 1 -TRICHLORDETHANE
I,|-D1CHLOK0ETHAHE
I.I. 2-TR1CHLOKOETHANE
CHLOROFORM
I • I -AICHLOKOETHTLENE
I.2-TRAN8-PICHLOROETHTLENE
ETHVLDENZENE
HCTHTLENE. CHLORIDE
TftlCHLOROFLUOROHETHANE
TETRACHLOROETHTLENE
TOLUENE
TRICHLOHDCTHTLENC
VINYL CHLORIDE
2r4t A-IRICHLOHOPHtNOL
PAftACHLORPMETA CREBOL
2-CHLOKOPftENOL
2.4-IiICHLaR0PHEHOL
2.4-DIHETHrLPHEHOL
4-NirROPHEHOL
PEN T AC HLOROPHCNOL
PHENOL
ACENAPHTHENE
li2.4-TRICHLORO»ENZENE
l.2-OICHlORfl&tNZENE
I.3-DICHLUR06EMZENE
li4-DICHLOHO[lENZENE
FLUOftANTHENE
NAPHTHALENE
»IB(2-ETHrLIIEXTL> PHTMALATE
ANTHRACENE
FLUOfcENE
POLLUTANTS NOT LISTED UEKE NOT DETECTED AT ANT SAMPLE POINT ON S1/O3/07
L-LESS THAN) O'OftEAUK IMANI T«TRACEl I OR J- INTERFERENCE I U -UNCONFIRMED I
N-Ii-NOT HE TEC Till.
ACID EXTRACT
*A8t-HtUTRAL8
UNITS
HO/L
NO/L
NO/L
HO/L
UO/L
MO/L
HO/L
MO/L
MO/L
HO/L
MO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
300
47B
• 40
4*
870
14*0
1010
9*1
372
31?
IS
3*0
34
N-D
II
144
N-P
N-D
III
II
4
30
104
3
13
337
N-D
440
1
2
N-D
4
N-0
3t
f
170
N-D
9
N-D
2
N-D
N-D
37
3
N-D
N-D
SECONDARY
EFFLUENT
*7
43
230
*
400
1020
t7«
174
13S
It
9
100
13
S
N-D
43
N-D
N-D
at
3
N-D
22
VI
4
23
170
7
N-D
N-D
I
1
N-D
a
22
N-D
1
N-D
3
N-D'
3
N-D
H-D
H-D
N-D
N-D
N-D
PERCENT
REMOVAL
7S
fl
70
ss
34
32
3
71
4f
S*
30
72
42
-
*»»
93
-
.
4S
73
t»t
34
13
-
-
92
-
*»+
m
-
-
w
-
3V
m
«4
_
40
-
-
-
-
W
ft*
-
-
PRIHAR1
EFFLUENT
230
240
•20
32
tao
1340
1100
924
340
IB4
14
300
27
N-D
N-»
249
N-D
10
»»
14
2
119
103
2
114
319
33
N-D
1
N-D
N-D
4
N-D
N-D
7
234
N-D
3 .
H-D
1
2
N-D
47
11
N-D
N-D
PftlHAM
8LUDOE
2»00
32700
30000
13?
1130
23*00
1130
13400
300
13100
21
1400
7»
N-D
130
230
140
400
»7
N-D
N-D
140
140
H-D
N-D
2400
a 30
N-D
H-D
N-D
N-D
H-D
N-D
N-D
N-D
220
100
1100
140
H-D
74
440
1200
1100
*2
120
SECOND ART
SLUtfOE
1400
• 710
14000
•31
413
*440
790
4B*0
100
4710
13
410
N-
N-
N-
70
N-
N-
40
N-
N-
210
470
N-D
41
330
33
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
ISO
H-D
N-D
N-D
»4
1*0
N-D
N-D
N-D
-------
DAILY ANALYTICAL RESULTS
CHATTANOODA
SAMPLE DATE ENblHO 81/03/07 0800 HOURS
FRACTION
BASE-NEUTRALS
NET ALB
Ul
NON-CONV. HETAL8
PARAMETER
PHENANTHRENE
AHTIHONT
ARSENIC
•ERTLLIUH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
MAGNESIUM
HANOAHE8E
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UHIT8
UO/L
UO/l
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
no/i
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
UO/L
UO/L
INFLUENT
N-D
17
10
I
L S
HO
33
37
L SO
L 300
94
7
340
5980
120
140
S3
24
3380
»
300
L 10
24*
SO
7
L 3
SECONDARY
EFFLUENT
N-D
L 10
L 10
L 1
L 3
37
L 70
SB
L SO
L 300
L SO
1
32
S20
27
07
47
21
340
0
210
II
2S4
74
L 9
L 3
PERCENT
REMOVAL
-
41
-
47
-
74
-
-
-
-
7
•6
70
ri
77
30
11
It
tO
11
30
-
-
-
2»
-
PR I HART
EFFLUENT
N-D
L 10
10
1
L 9
140
44
37
It
400
40
S
230
4320
120
140
34
32
2300
»
300
L 10
23»
L 30
4
12
PRIMARY
BLUOOC
2VO
140
420
43
310
ISOOO
•900
»33
4400
24000
2400
•30
2BOOO
HOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
SECONDARY
SLUDOE
N-D
L 00
30
24
110
3400
1400
172
1000
L 4000
780
230
3000
HOT RUN
NOT RUN
HOT RUH
HOT RUH
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUH
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON 01/03/07
L'LESS THANI 0*OREATEA THANI T-IRACEI I OR J-INTERFERENCE! UMINCONFIRHEDI
N-ti'HOI DETECTED.
-------
HAILY ANALYTICAL KE6ULT8
CHAITANUODA
SAMPLE DA1E E HOI NO 81/03/00 0*00 HOUR!
FRACTION
CONVENTIONAL!
PARAHEIEK
• Oil
TOTAL SUSP. BOLIDB
COD
OIL I OMEABE
NON-CONVENT10NAL8 TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIS9, SOLIDS
TOTAL VOL, BUS, SOLIDS
AHHONIA NITROGEN
IDC
VOLATILEB
ON
ACID EXTRACT
BASE-NEUTRALS
METALS
BENZENE
Ii1i1-TRICHLOROETHANE
I.I.2-IRICHLOROETHANE
l>li2>2-IETRACHLOROETHANE
CHLOROFORh
I12-TRANB-DICHLOROETHYLENE
EIlirLBENZENE
I1ETMYLENE CHLORIDE
TRICHLOROFLUOROHE T HANE
TETftACHLOROCTHYLENE
TOLUENE
TRICHLOROETHYLENE
VINYL CHLORIDE
2<4i4-IRICHLOROPHENOL
PAftACHLORONETA CRESOL
2<4-[i|CHLOROfHENOL
2<4-DIHCTNYLPHENOL
4-NITROPIIENOL
PENTACNLOROPIIENOL
PHENOL
ftEMZIDINE
I.2>4-TRICHLOROBENZENE
I>1-OICHLORO»ENZENE
l.4-blCHlOHO»rNZENE
FLUORANTIIENE
NAPHTHALENE
biai2-EIHYLHEXYL> PHIHALATE
AHTHRACENE
PHENANTIIKENC
HYKtNE
AHIIHONir
AkStHIC
htftfLLIUN
UNITS
nb/L
HO/L
NO/L
NO/L
UO/L
NO/L
HQ/L
HO/L
NO/L
NO/L
NO/L
HO/I
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UD/L
UO/L
UO/L
UO/L
UO/L
UC/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUE
400
171
140
as
870
941
790
419
290
129
20
410
19
M-D
H-0
N-D
9V
2
17
7t
1
24
29t
14
N-D
1
1
7
N-D
N-D
N-D
1*2
N-D
7
N-D
N-D
N-D
11
4
I
1
N-D
L 10
L 10
L 1
SECOND'
NT EFFLUEI
41
11
240
2
If]
• 7»
• 41
144
111
21
•
•2
4
1
N-D
3
47
N-D
II
112
2
9
71
4
N-B
N-D
N-D
7
N-»
11
2
42
N-D
4
1
1
N-D
H-D
N-D
N-D
H-tt
N-D
L 10
L 10
L 1
IRT PEfcCEl
IT REMOV4
• 4
•2
44
92
78
ff
-
40
92
78
40
81
40
-
-
-
20
99*
39
-
33
• I
73
71
-
»»»
99*
-
-
-
-
48
_
43
-
-
-
m
99*
99*
99*
-
-
-
-
IT FftlNARY
IL EFFLUEN
410
17»
990
If
170
t44
784
284
174
110
18
299
14
8
N-D
N-D
99
2
N-D
70
3
23
211
N-D
14
N-P
N-D
8
10
N-D
N-D
223
12
N-D
2
1
N-0
25
9
1
1
N-D
L 10
L 10
3
PRIHAR1
T 8LUOOE
12000
24300
18000
730
1400
29900
1200
14900
440
14100
29
790
29
12
110
N-D
84
N-D
110
N-D
N-D
N-D
440
230
N-D
N-
N-
N-
N-
N-
N-
180
N-D
100
N-D
N-D
110
140
N-D
N-D
80
90
140
190
190
r •£(
8LI
90(
88!
IK
29;
22i
991
71(
481
I7<
47S
12
49<
N-
N-
N-
N-
N-
N-
N-
10
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
90
N-
N-
N-
20
N-
N-
N-
N-
L 80
27
12
OHDARV
JDOE
10
10
>00
'0
1
10
)
to
>
to
)
POLLUTANTS NOT LIBIEIi MEM NOT DETECTED AT ANY 8AHPLE POINT ON BI/01/OB
L-LESS THANI O-QKEATER IHANI T-TRACEI i OR J*INTERFEREHCE* UMMCONFIRNEDI
N-li-NOI ('EfCCTED.
-------
liAILT ANALYTICAL RESULTS
CHATIANOOOA
SAMPLE PATE EHI>INO 81/03/08 0900 HOURS
FRACTION
HE1ALS
MON-CONV. HETALS
o
-J
PARAMETER
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
MAGNESIUM
HANOANE8E
SODIUM
TITANIUM
YTTRIUM
UNITS
UO/L L
UO/l
UO/L
UO/l
UO/l L
NO/I
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
MO/L
UO/L
UO/L L
INFLUENT
3 L
2920
110
44
SO L
100 L
37 L
2 L
210
4120
tJ
100
31
10
IIVO
9
200
170
47
3 L
SECONDARY
EFFLUENT
3
430
11
33
30
300
30
1
30
340
it
73
49
12
310
9
220
224
81
3
PERCENT
REMOVAL
L
OS
BO
24
L
-
12
30
74
12
73
27
4
-
74
-
21
-
-
-
PRIMARY
CFFLUENT
3
3040
93
41
30
300
43
3
200
4420
110
110
S3
II
1940
10
320
177
39
9
PRIMARY
SLUDOE
I BO
31000
9*00
117
4400
18000
2400
420
24000
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
SECONDARY
SLUDOE
90
12000
1300
90
1000
L 4000
720
210
4400
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
(•01101 AMIS HO! lIBIttl HERE HOT HE1ECTED AT ANY SAMPLE POINT OH BI/O3/OB
I-LESS THANI 0-GktAIEfc THAN I T-TftACEl I OR J-1HTERFERENCEI U-UMCONFIRHEDI
H D-HOF HFTECTEH.
-------
DAILY ANALYTICAL KEKULTB
CHAUAMODUA
SAMPLE DATE CNDINO B1/03/6V 0800 HOURS
rRAtTION PAKAHETER
CUNVtNTIUNAItl HOB
TOTAL SUSP. SOL ins
cou
OIL I DKEABE
NOM-CUNVENTIOMAL8 I01AL PHtMOLS
TOTAL SOL I US
TOTAL K16S. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE HISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
VOI.AIJI IS
00
ACIb EXTKACI
• ASE-NEUTNAI.8
ItCIALS
»ENZENE
til>l-TRlCHLOItOETHANE
1>I>2-1RICHLOROETNANE
CHLOROFORM
I>2-TRAHS-PICHLOROETHTLEHE
ETHYLKEHZENE
HETHYLENE CHLORIDE
TRI CHI. OkOFLUOhOHE THAHE
TOLUENE
TRICIILOROEIHYLENE
2-CMLOKOPIIENOL
2.4-btCHtOROPHENOL
PHENOL
ACENAPHTHENE
1>2>4-TR!CHL0RO»ENIENE
1 f 2-DICHLOROBENZENE
1>3-DICHLOROIIEHZENE
1 >4-DICHLOROkENZENE
fLUORANTHENE
JBOPMOMWE
NAPHTHALENE
VIS<2-ETHYLHEXYL) PHTHALATE
DI-N-kUTYL PHTHALATE
DUTHYL PHTHALATE
CIIRYSENE
ACENAPIIIHYLENE
ANTHRACENE
FLUORENE
PHENAHTHRENE
PYRENE
AHUHONY
ARSENIC
UNITS
HO/L
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UQ/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
SECONDARY PERCENT PRIMARY PRIMARY SECONDARY
INFLUENT EFFLUENT REMOVAL EFFLUENT SLUDGE SLUDOE
13f
340
14
1030
777
438
303
to
103
22
130
29
4
N-D
24
2
• 14
40
3
9
937
»
1
31
271
N-D
4
N-D
1
N-0
2
N-D
17
8
9
3
H~D
4
1
N-D
1
t
L 10
L 10
21
20
tie
7
28
444
424
84
70
14
t
27
3
t
N-D
11
N-B
N-B
37
2
K-B
12
M-B
M-D
4
1
M-B
3
M-
M-
N-
N-
M-
H-B
M-B
M-D
4
M-D
M-D
N-D
N-D
N-0
N-D
L 10
L 10
Is
4f
34
»7
|7
jf'
38
2f
as
99
83
88
83
-
94
m
m
38
40
m
fB
99t
m
81
m
-
23
~
99*
-
99*
-
99 1
99*
99*
20
-
99*
99 f
-
99 1
99*
_
-
220
120
340
9
930
794
474
188
112
74
23
130
23
4
N-0
20
3
22
92
J
17
919
12
N-B
29
224
N-0
a
N-D
2
N-D
2
34
18
17
N-D
N-B
M-D
4
N-D
N-B
N-B
2
L 10
L 10
9200
13300
31000
3210
1400
14200
940
7980
330
74SO
31
1300
N-0
M-D
40
N-D
N-0
44
29
H-D
N-D
310
110
N-D
M-D
390
87
780
140
M-D
130
320
H-D
970
H-D
N-0
N-D
73
N-0
49
47
199
243
140
390
3400
9990
100000
488
73
4340
940
4430
140
4290
II
430
M-D
M-
M-
M-
H-
M-
N-
M-
M-
N-
M-
M-
N-
H-
N-
M-
M-
M-
M-
N-
N-
M-
M-
M-
M-
M-
M-
M-
N-
M-
H-
L 80
40
POLLUTANTS NOT LIKUD UEKE NOT HETECTEV AT ANT SAMPLE POINT OH 81/03/0*
L'LESS HIAHI 0-GREATEH THAN* I-TRACEI t OR J-IHTERFEftENCEl U-UNCONFIRHEDI
N-I'-HOl liETECTED.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE PATE ENOIMB Bl/03/0* 0800 HOURS
FRACTION
HETALB
NDM-CONV. HETALI
PARAMETER
BERYLLIUH
CADHIUN
CHROMIUM
COPPER
CYANIDE
LEAB
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
MAGNESIUM
MANOANE8E
SOBI UN
TITANIUM
YTTRIUM
UNITS
00/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
NO/L
UO/L
UO/L
HO/L
UQ/L
NO/L
UO/L
UO/L
INFLUENT
L
L
L
L
L
L
L
1
9
32
Jf
10
90
300
SO
2
100
3110
72
72
4t
II
1100
7
320
140
94
a
L
L
L
L
L
L
L
L
SECONDARY PERCENT PRIMARY PRIMARY
EFFLUENT RENOVAL EFFLUENT 8LUDOE
1
9
110
10
40
SO
300
90
1
19
240
24
39
46
8
31
8
240
194
99
9
.
-
-
74
-
-
-
-
90
43
f2
47
91
2
27
»B
-
29
_
2
-
L 1
L 9
47
42
L 10
L 80
L 300
L 90
2
140
4280
80
44
94
10
1370
•
390
197
140
8
110
270
33000
11000
1940
4400
43000 L
2BOO
440
30000
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
BLUDOE
24
90
14000
1300
181
840
4000
790
190
3800
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON 01/03/09
L-I.ESB TMANI O-GREATEK IIIANI T-TRACEI i OR J-INURFERENCEI U-UNCONFIRHEBI
N-P-NOT
-------
PAIL* ANALYTICAL RESULTS
CHAUAMOOOA
ADDITIONAL SAMPLE POINTS
SAMPLE PATE ENDING 81/01/0* 0800 HOURS
FRACTION
CONVENT IONALB
PARAMETER
TOTAL KUHP. SOL IPS
CUli
OIL I OftEABE
HOM-CONVEMIIONAL8 TOTAL PHENOLS
TOTAL SOL IBB.
TOIAL HISS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE D18S. SOL IBB
TOTAL VOL. BUS. SOLIDS
AHHOMIA M1TROOCN
TOC
VOLATILC8
ACID EXTRACT
HASE-NEUIRALS
bENZENE
CHLOROBENZEHE
l.l.t-TRICHLOROETHANE
lil-DICHLOROETHANE
CHLOROFORM
I > 2-TRAN8-BICHLORQETHYLENE
CTHYLBCH2ENE/
METIIYLCNE CHLORIDE
BICIILOftOBkONOHETHANE
TRICHLOROFLOOfiOHETHANE
TOIUENE
PHENOL
I.2.4-TR1CMLOROȣNUNE
I.1-DICHLORO*ENZENE
li4-DICHLOFtaBCHZENE
FLUORAMTHENE
NAPHrNALCNE
N-NITROSDDIPHEHYLAHINE
BI8<2-ETHYLHEm> PMTMALAtE
DI-N-BUIYL PHIHALATE
61-N-OCITL PHTHALATE
BIETHY1. PIU(MLAT£
1,2- HEN/ANTHRACENE
ANTIIftACEHE
FLUORENE
PIIENANTHRENE
ANIlNOMir
ARSENIC
BERYLLIUM
HEIAI8
CHROHIUN
COPPER
POLLUTANTS NOT LISTED WERE MOT DETECTED AT ANY SAMPLE POINT OH 81/03/0*
L-IESS THAMJ C»OREAIER TMA«» T-TJ*ACE> I OK J*INTERFERENC£I U'UNCONFIRHEOI
N-D>NOI DETECTED.
UNITS
HO/L
HB/L
HO/L
HO/L
UB/L
NO/L
HO /I
no/L
NO/L
HO/L
NO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UB/L L
UO/L
UO/L L
UO/L L
UO/L
UO/L
VACUUM FILTER
FILTRATE
4*
37»
a 10
30
148
2110
1910
ait
114
109
63
120
a
N-D
t
N-D
N-D
N-D
a
14
N-P
a
ti
N-B
N-D
1
H-P
N-B
N-B
N-D
A
N-B
3
9
N-D
1
N-D
1
10
10
1
s
14
40
UIOEBTEft
SUPERNATANT
970
auo
2200
U2
240
1900
llfO
U70
447
1220
92
80S
8
28
1
*
N-e
10
217
14
N-D
a
171
40
10
II
12
14
131
If
117
11
28
N-J>
1
20
If
20
10
110
3
29
970
710
TAP
UATEK
L 1
2
L 23
4
L 3
113
III
40
40
L 2
L 1
1
N-D
H-It
1
N-B
28
N-D
N-B
14
1
2
7
N-D
N-D
N-D
N-D
N-D
N-fi
N-B
234
H-0
14
N-D
N-D
N-D
N-B
N-D
L 10
L 10
L 1
L 3
L 10
L 10
-------
UA1LY ANALYTICAL RESULTS
CIIAUANOOOA
ADDITIONAL SAMPLE POINTS
BAMPLE DATE CHUIHO 81/03/07 0800 HOURS
FRACTION PARAMETER
n
oo
HE1AL9 CYANIDE
LEAD
MERCURY
NICKEL
BILVEft
ZINC
NON-CONV. METALS ALUMINUM
•AftlUM
fcOROM
CALCIUM
CUMLT
IRON
HAONEBIUH
NANOANE8E
HOLYfrDEHUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
UNITS
UO/L
IIO/L
MO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
no/1.
UO/L
UO/L
MO/L
UO/L
UO/L
MO/L
UO/L
UO/L
UO/L
L
L
L
L
L
L
L
VACUUM FILTER
FILTAATE
10
30
100
so
2
110
2MO
HO
ISO
311
1
2920
42
1740
10
277
SO
s
II
t'lOESTER
SUPERNATANT
32
4 BO
3600
3*0
13
2420
38200
1140
220
35*
*7
28800
43
3400
33
273
L SO
43
460
TAP
WATER
L 10
L 30
L 300
L 30
t 1
IB
L 40
21
L 20
24
L S
L 30
4
L 10
L 10
1
94
L 3
L 3
PUtt UTAH IB NOI LISICI. WERE MOT liETECIED AT ANY SAMPLE POINT ON B1/03/OP
L-LESS THAHI O-OREAIER THANI T-TRACEI I OR J-INTERFERENCE I U-UNCOHFIRNEDI
H-Ii-NOT I'ETECTED.
-------
DAILY ANALYTICAL RESULTI
CHATTAMOOOA
•AMPLE liATE ENDING BI/03/10 0800 HOUM
FRACTION
CONVEMIIQNALB
PARAMETER
• OD
TOTAL 8UBP
COD
OIL I OREABE
SOLIDS
00
ro
NOM-CONVENTlONALi TOTAL PHENOLS
TOIAL BOLIDS
10ML DI8S. 80LIDB
10IAL VOLATILE IOLIDI
VOLATILE DIS9. BOLIIH
TOTAL VOL, SU3. BOLIPB
AMMONIA NITftOOEM
TOC
VOLATILE* »ENZENE
i > i > i -TMICHL-OKOE THANE
lil-DICHLOROETHANE
I•Ii2-TRICHLOftOETHAHC
CHLOROFORM
Ii2-rRANB-PICHLOROETHVLEHE
CIHTLBENZENE
METHYLEHE CHLORIDE
TRICHLOROFLUOROHETHANE
TCIRACHCOROeTHYLENE
TOLUENE
TNICHLOROEIHYLENE
2>4-DICHLOKOPHENOL
PHENOL
1>2>4-TRICHLORODENZEHE
lf2-PICHLORO»ENlENE
Irl-PICHLOROBENZEME
li4-DICHLOROiiENZENE
FLUORANTHENE
HAPHTHALEME
ANTHHACENE
FLUI1RENE
PHENAHTHRENE
METALS AHTIHONr
ARSENIC
HEiiYLLlUn
CADNIUH
CHROMIUM
COPPER
CYAN1HE
LEAD
MERCURY
NICKEL
PULLUIANIS NOT LISIED UCRC HOI DETECTED AT ANY 8AHPLE POINT ON 81/03/10
L-IESS IHANI O'UREAIEN THAN! I-TRACE) I OR J'INTERFCRENCEI U-UMCOHFIRMEDI
N-li-HOI DETECIfD.
ACIO EXTRACT
HASE-NEUIRAL8
UNIT!
HO/L
MO/L
HO/L
HO/L
UO/L
MO/L
HO/L
MO/L
HO/L
NO/L
MO/L
MO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
SECONDARY PERCENT PRIMARY PRIMARY SECONDARY
INFLUENT EFFLUENT REMOVAL EFFLUENT BlUPOE ItUOOE
440
119
740
22
1220
1120
1000
341
194
209
1?
300
13
7
7
N-B
124
2
74
41
2
21
280
7
•
207
7
N-P
1
' 9
N-0
39
H-D
M-0
N-P
L 10
14
L 1
9
l»0
»•
141
L 90
400
91
39
24
140
II
71
tio
704
99
40
19
12
41
1
2
N-B
N-P
90
N-P
•
27
1
2
39
1
•
19
1
N-
N-
1
N-
H-
H-
N-
N-
L 10
L 10
1 I
L 9
40
12
III
L SO
L 300
L 90
f2
•2
•1
90
»4
It
21
•9
H
ti
it
•0
77
71
W
-
40
ft*
•f
94
90
»l
00
•4
_
»s
97
-
tt*
BO
-
t»*
-
-
-
^
27
-
-
79
a*
it
-
90
4
330
202
700
14
1200
1270
1070
210
172
114
It
240
13
4
1
M-D
tor
2
37
42
1
II
201
7
M-0
3t3
t
N-P
4
»
N-
N-
N-
N-
N-
L 10
II
L 1
L 9
200
T2
71
L 90
400
94
11000
7100
49000
tot
1190
•940
1100
9140
340
4000
33
3000
29
N-0
N-»
93
100
N-P
70
N-P
N-0
N-0
740
140
N-0
340
•00
»4
N-0
140
940
too
too
120
280
120
230
42
270
21000
10000
1410
9tOO
•9000
2tOO
3000
7340
10000
111
113
7*10
9?0
9410
100
9330
12
300
N-P
*-»
N-
N-
29
N-
N-
N-
N-
N-
N-
«-
N-
H-
t4
N-
N-
N-
N-
74
N-
N-
H-
L 00
40
20
to
14000
1400
242
1000
L 4OOO
790
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE PATE EHDINO 81/01/10 OBOO HOURS
FRACTION
METALS
NON-CONV, METALS
O
00
CO
PARAMETER
SILVER
2INC
ALUMINUM
MR lUH
•ORON
CALCIUM
COIALT
IRON
MAGNESIUM
MANGANESE
SODIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L
INFLUENT
»
930
SECONDARY
EFFLUENT
1
fj
PERCENT
REMOVAL
at
•2
PRIMARY
EFFLUENT
10
1*0
PRIMARY
SLUDOE
840
13000
SECONDARY
SLUDOE
180
4000
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
HO/L
UO/L
HO/L
UO/L
UO/L
f030
ISO
120
92
22
4440
6
430
277
L S
310
28
»8
SO
7
140
•
240
212
L 9
L 9
ft
81
18
4
is
»7
40
U
44
9440
130
190
92
17
2*80
8
110
273
L 9
8
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
PDLLUfANIS N01 LISTED WERE NOT DETECTED AT ANY SAMPLE POINT ON Bl/03/10
L-LESS THAN) 0-ORCATER I MAN I T-TRACEI I OR ./'INTERFERENCE! U'UNCONFIRMEOI
N-I'-MOT 1'EUCTFP.
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE l>*tf ENDING ttl/01/II OBOO HOUR!
IKAC1ION
CONVENTIONAL!*
PARAMETER
HUP
10TAL SUSP
COP
OIL I ORLA8E
8ULID8
n
oo
NON-CONVENTIONALS IOTAL fllEMOI.S
IOTAL SULIDS
TOTAL PI83. SOLIDS
TOTAL VOLATILE SOL IPS
VOLATILE PICS. SOLIDS
TOTAL VOL. 808. SOLIDS
AHMONIA NITROOEN
TOC
VOLAFILES SENZENE
CARDOH TETRACHLORIDE
CHLOROtENZENE
111.I-TRICHLOROETHANC
Itl-DICHLOROETHANE
1.1.2- TRICIIL OROE THANE
CMLOROFORH
I.2-TRAN8-DICHLOROETHYLENE
EIHYLtENZENE
HETHYLEHE CHLORIPE
TRICHLOROFLUOROHETHANE
tEIRACIILOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2i1'i-TRICIII.OROPHEHOL
PARACHLUROHETA ChCSOL
2M-DICHLOROPHENOL
2>4-DIHETHYlPNENOL
2-NITROPHENOL
PENIACHLOROPHCNOL
PHENOL
lt2>4-TRICNLOHO»EHZENE
lr2-PICIIlQftp»ENZENE
t>3-Ii|CIILOKp»ENZENE
Ii4-DICHLOROBENZENE
FIUORAN1HENE
NAF-HTHAIENE
I>2-»EHZANTMRACENE
II>I2-BENZOFLUORANTHENE
CHRVSINE
ACk'NAPllTMYLENE
ANTHKACENE
FLUORENE
PIIENANINKENE
POLLUIANIS NOI LISTED UEKE NOT DETECTED AT ANY SAHPLE POINT ON 01/03/11
I-LESS THAN* 0-OREAUR IHANI T-IRACEI I OR J-IHTEkFEKENCEl U«UNCOHFIRHED»
H-P'NOr DCtECfED.
ACID EXTRACT
VASE-NEUTRALS
UNI1S
no/L
HO/L
HO/L
HO/L
UO/L
NO/L
HO/L
HO/L
HO/L
HO/L
HO/L
HO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUENT
440
113
900
4S L
1100
1570
1240
323
912
211
IS
349
14
H-li
N-D
II
N-0
H-D
121
N-0
34
71
2
2U
23*
t
2
4
II
21
N-0
11
A4«
9 '
N-D
10
N-
N-
30
H-
N-
N-
H-
M-
N-
N-
SECOMIiAftY PERCENT
EFFLUENT REHOVAL
31 OS
12 »0
210 77
2 »4
279 79
10*0 12
1010 17
112 7*
•4 71
2S S7
12 31
73 7i
4 71
N-»
«-»
2 S2
N-0
H-D
92 97
N-D r
a s«
IS 41
1 90
41 SO
<• «l
i ar
N- 19 1
N- m
12
17 If
N-
N- »t»
12 80
N- m
N-
N- m
M-
N-
N- »y»
N-
N-
H-
H-
»-
N-
N-
FR1HART
EFFLUENT
400
24»
• 70
13
I1BO
I9AO
1190
424
2*2
112
If
330
14
1
2
1
1
N-D
117
2
37
9«
1
240
233
10
N-D
N-D
10
31
78
N-D
731
N-
H-
12
N-
M-
N-
N-
N-
M-
N-
N-
N-
N-
f HI NARY
SLUDOE
II 000
2f300
41000
If SO
2100
11 000
1420
moo
4*0
IS100
14
2200
N-D
H-D
N-D
N-D
N-D
170
• 7
N-D
• 1
N-D
N-D
N-D
410
1000
N-
N-
N-
N-
N-
H-
340
1200
190
N-D
110
4oo
4000
f2
•4
120
• 0
to
ISO
1*0
SECONDARY
•IUDOE
1400
fOlO
12000
4Df
2*1
fMO
•20
7290
130
7120
14
470
N-
N-
N-
N-
N-
M-
N-
N-
N-
N-
N-
2*
N-
33
N-
N-
H-
N-
N-
H-
N-
fa
N-
N-
H-
10
fS
N-
H-
N-
N-
N-
N-
N-
-------
DAILY ANALYTICAL RE8ULIB
CHATTANOOOA
SAMPLE DATE EMU I HO 01/03/11 0800 HOURS
FRACTION
BASE-NEUTRALS
METALS
00
Ln
NON-CONV. METALS
PARAMETER
PYftEME
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
IOROM
CALCIUM
COBALT
IRON
HAOHESIUH
HANOANESC
SODIUM
VANADIUM
YTTRIUM
UNITS
UO/L
UO/L L
UO/L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L L
NO/L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L
HO/L
UO/L
UO/L
MO/L
UO/L
HO/L
UO/L
UO/L L
INFLUENT
N-D
10
14
1
4
160
100
MB
90
SOO
90
0
930
3300
MO
170
40
II
4210
»
100
140
f
3
L
L
L
L
L
L
L
L
SECONDARY
EFFLUENT
M-D
10
14
1
3
43
19
102
30
100
30
2
130
300
27
100
44
II
290
•
230
317
9
3
PERCENT
REMOVAL
-
.
-
-
17
72
• 3
11
-
40
-
73
74
VI
01
41
0
-
VI
II
21
12
44
-
L
L
L
L
L
L
L
PRIMARY
EFFLUENT
H-0
10
10
1
9
140
fO
111
30
100
30
S
470
9440
140
IfO
4?
f
1020
»
110
384
3
3
PRIMARY
8LUOOE
100
120
480
31
290
20000
0300
914
AiOO
33000
2«00
810
J«000
NOT RUN
NOT MUM
HOT RUM
HOT RUN
HOT RUM
NOT RUN
HOT RUM
NOT RUN
HOT RUM
NOT RUM
NOT RUN
SECONDARY
SLUDOE
N-D
L 80
30
22
100
9400
1100
148
930
L 4000
270
190
3000
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUH
NOT RUN
NOT RUN
NOT RUN
HOT RUN
PUILU1AMIS NOT LIBIIU MERE NOT DETECTED AT ANY SAMPLE POINT ON 81/03/11
I-LESS fMANI 0-OftEATEft III AN I I-TftACEl I OR J- INIERFERENCE • U-UHCONF IRM£»I
N-li-NOI IIETtCTEIi.
-------
PAILT ANALYTICAL RESULTS
CHATTANOOOA
SAMPLE DATE ENDING 01/03/12 0000 HOUR*
FRACTION
CONVENT IONALB
PARAMETER
kOP
TOTAL SUSP
COO
OIL I UREA8E
SOL IPS
n
oo
NON-COMVCMMONMS TOTAL PHENOLS
TOTAL 80LID8
IOTAL OI8B. SOLIDS
TOIAI. VOLATILE SOLID!
VOLATILE DISS, SOLIDS
TOTAL VOL. SUV. 80LIP8
AHHONIA NITROOEN
IOC
VOLATILE!! SENZENE
CAMION TETRACHLORIPE
CHLOftOIEHZENE
•Itl-tftlCHLOftOETHAHE
•I-PICHLORDETHANE
.li2-TRICHLOfcOETHAHE
HLOROFORH
• 1-PlCHLOftOtTHUEHE
r2-TftAN8-01CHLOftOETHVLENE
•2-PlCHLOROPftOPAHE
. 3-DICMLOROPKOmENE
ETHUVEHZEHE .
METHYLENE CIILOKIPE
Tft I till OROFLUQftONE THAME
CMl ORODI»ROnOHETHANE
IE TR ACHL OROE TIITL EHE
TOLUtHE
1K1CIILOKUEIHYLENE
ACIP EXTRACT PAftACHLUROHETA CRE90L
2r4-DICHLOROPHENOL
2'4-DinETHYLFHENQL
PENTACHLOROPHEMOL
PHENOL
BABE-NEUTRALS 1.2.4-IR1CHLOftOIEHZENE
Ir2-PICIU OROfrENZEME
It1-PICHLORUBEHZENE
l.4"PICIUOROt£NZEN£
flUORANTHENE
NAPIIUIALENE
msiz-ETHriiiExrL) PHTHALAIE
1I>I2-*ENZOFLUORANTHENE
COMBINE
ANTHRACENE
FLUURENE
POLLUIANTB NOT LIbItU WERE NOT DETECTEP AT ANT SAMPLE POINT ON 81/01/12
L-LEB8 TIIANI O-GREAICR THAN! I-TRACEI I OR J-1NTERFERENCEI U-UNCONFIftHEOI
N-b-NOr PEUCTEII,
UNITS
NO/L
HO/L
HO/L
HO/L
UO/L
HO/L
HO/L
HO/L
NO/L
HO/L
HO/L
HD/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UU/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
UO/L
10/L
Uu/L
UO/L
UO/L
UO/L
UO/L
UO/L
INFLUEN
429
17V
1100
22
»50
ISVO
1210
911
292
2BI
IB
409
14
1
4
10
2
1
100
1
3
1
1
30
140
1
1
74
2VO
10
N-D
S
13
N-0
434
N-D
H-D
1
V
N-D
1*
H-D
N-D
N-D
N-D
N-D
SECOND*
f EFFLUEH
94
IB
290
V
ISl
1290
1210
214
204
32
10
to
4
H-D
2
3
H-B
H-D
19
N-
H-
H-
N-
7
2V
H-
H-
13
40
1
N-D
a
n
N-D
44
N-D
N-D
9
N-D
N-D
19
N-D
H-D
N-D
H-D
N-0
RY PERCENT
T REMOVAL
VI
•0
77
at
Bl
21
-
94
IV
Bf
44
7«
71
VVt
90
70
VVt
vvt
45
Wt
vvt
VVi
vvt
77
7V "
»»f
vvt
Bl
B4
VO
.
-
19
.
VO
_
-
-
VVi
.
21
-
.
-
-
-
EFFLUCN
470
297
B70
11
1090
1990
I2VO
4V4
114
17B
|V
149
19
H-D
N-D
19
2
H-D
110
N-D
2
H-P
H-D
12
41
1
N-D
170
300
t
2
V
17
4
741
N-D
N-D
1
t
N-D
21
N-D
N-D
H-D
N-D
H-D
PRIMARY
t BLUDOC
4VOO
4V40
4SOOO
VVI
1400
4140
1400
1990
300
1290
IB
1900
N-D
N-D
N-
N-
N-
12
41
N-
N-
H-
H-
74
H-
N-
H-
49
370
490
N-D
H-D
H-D
N-D
900
1900
230
N-D
VO
300
1400
110
120
B4
48
140
SEC
ILL
340
374
I3C
47]
290
479
101
2Vi
140
282
IB
140
N-l
H-
H-
H-
N-
N-
29
N-
N-
N-
N-
N-
N-
N-
H-
N-
N-
N-
N-
H-
H-
N-
N-
24
N-
N-
N-
N-
27
N-
N-
N-
N-
N-
ONDAHY
DOE
0
0
00
0
0
0
0
-------
DAILY ANALYTICAL RESULTS
CHATTANOOGA
SAMPLE DATE ENDINO 81/03/12 0800 HOURS
FRACTION
DA8E-NEUIRAI.B
METALS
00
NON-CONV. HETA18
PARAMETER
PHENAHTIIRENE
ANTIMONY
ARSENIC
IERYLLIUH
CADHIUN
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
DARIUN
DORON
CALCIUM
COBALT
IRON
MAGNESIUM
MANOANE8E
80DIUN
VANADIUM
YTTRIUM
UNIT!
UO/L
UO/L L
UO/L L
UO/L L
UO/L
UO/L
UO/L
UO/L
UO/L L
NO/L
UO/L
UO/L
UO/L
UO/L
Ufl/L
UO/L
HO/L
UO/L
UO/L
flO/L
UO/L
HO/L
UO/L
UO/L L
INFLUENT
M-D
10
10
t
4
110
100
00
so
100
190
0
920
9080
140
IfO
47
19
1200
0
100
2»f
0
9
L
L
L
L
L
L
L
SECONDARY
EFFLUENT
N-0
10
10
t
9
40
22
07
SO
300
too
1
110
470
27
UO
44
10
320
0
220
34f
S
9
PERCENT
REMOVAL
-
-
-
-
17
44
70
-
-
.
71
00
7»
M
•>
U
4
31
to
-
27
-
30
-
PRIMARY
EFFLUENI
N-D
L 10
L 10
L 1
L 9
120
07
04
L 90
400
230
0
3fO
9440
130
200
30
12
2490
»
310
138
L 9
9
PRIMARY
8LUDOE
290
09
3*0
49
290
19000
OfOO
mo
9200
23000
4TOO
700
33000
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
SECONDARY
8LUDOE
N-D
L 00
30
24
100
II 000
1300
310
7tO
7000
1100
210
9100
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
POLLUTANTS HOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT ON 01/03/12
L-LE9S THAN I 0-OREATER THAN! T'TRACEI I OR J-INTERFCRENCEI U-UNCONFIRMEDI
N-D-HOT DETECTED.
-------
MASS BALANCE IN POUNDS f>ER DAY
FRACTION
CONVENTIONALB
NON-CONVENTIOMAL6
VULATILE8
ACID EXTRACT
BASE-NEUTRAL 8
PESIIC1DEU
METALS
PARAMETER
iOO
TOfAL 8UBP
COD
OIL 1 GREASE
FOR SAMPLE CATC CNDINO 800*14 AT 0000 HOURS
•OLIOS
TOfAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOL IPS
VOLATILE DI8S. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOO
BENZENE
CHLOROBENZENC
11111-TRIGHLOROETHANE
IiI-DICHLOROETHANE
CHLOROFORM
1(2-TRANS-DICHLOROCTHYLENE
ETHYLBENZENE
HETHYLCNE CHLORIDE
DICHLOROBftOHOHETHANE
DICHLORODIFLUOROHETHAME
TE TRACHLOROCTHYLENE
TOLUENE
TRICHLOROETHYLEHE
2f4i4-TRlCHLORDFHENOL
2H-IUCHLOROPHENOL
2i4-DinEIHYLPHENOL
PEMTACHLOROPHEMOL
PHENOL
li2>4-TRICHLOROBENZENE
1.3-DICHLORDBENZENE
1.3-DICHLOROBENZENE
t>4-PICHLOROBEMZENE
NAPHTHALENE
BISI2-ETHYLHEXYL) PHTHALATE
BUTYL BENZYL PHTHALAIE
bl-N-BUIVL PHTHALATE
DIETHYL PHTHALATE
DIHETHYL PHTHALATE
ANTHRACENE
HIENANIHRENE
OAHNA-BHC
ANIINONY
ARSENIC
BERYLLIUM
INFLUENT
20**1«
127 HI
413339
30711
303
483224
449312
84*49
7*448
474?
»37I2
1.?
M-D
8.4
M-ft
48.0
M-D
3.7
HOI RUN
N-D
N-D
74. f
78.7
.7
4.1
I.I
M-»
l.f
82.9
94. 2
l.»
H-D
.7
3.7
2.2
H-D
.7
I.I
N-D
1.1
I.I
1.3
3.4
l.f
.4
TOTAL*
OUT
18004*2
22*044
3888*1
18777
38,8
40*200
37*019
*94I4
193447
9798
2*3*7
_
-
-
-
.
-
_
.
-
.
-
-
-
H-»
1.0
2.7
N-D
3.4
1.0
H-D
.3
.3
I.I
3.4
1.0
.7
1.7
.7
H-D
N-D
N-D
2.0
2.7
N-D
EFFLUENT
*450*
»7B8
40794
479
27.3
337783
31497*
4**93
4090
9043
14174
NOT RUN
NOT RUN
NOT RUM
NOT RUH
NOT RUN
NOT RUN
NOT RUM
NOT RUM
NOT RUH
HOT RUH
NOT RUH
NOT RUM
NOT RUH
N-D
1.0
2.7
N-D
3.4
1.0
H-D
H-D
N-D
.3
2.7
1.0
.7
1.7
.7
N-D
H-0
N-D
2.0
1.0
N-D
PRIMARY
BLUPOE
90444
74294
1244U
13*28
1.1
81437
10710
7834
47342
44.4
2244
L .1
L .1
N-D
L .1
L .1
,
.
L .1
t .1
L .1
8
9.
S.
M-
M-
H-
N-
N-
H-
N-
.3
.3
.8
.*
N-
M-
M-
N-
N-
N-
H-B
L O.I
.7
N-D
SECONDARY
9LUDOE
1439337
143032
20191*
4174
•0-1
14*780
93724
37409
102099
448
12*99
H-l>
H-D
N-D
N-D
.3
N-B
.2
N-D
H-»
N-D
1.8
1.0
N-D
N-
H-
H-
H-
N-
N-
N-
H-
N-
H-
N-
H-
H-
H-
H-
H-
N-
H-D
N-D
1.0
N-D
* TOTAL MASS OUT IS NOT ADJUSTED BY HASB CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED UEKE NOT DETECTED AT ANY SAMPLE POINT
L'LCBS THANI N-P-MOT PEItCTEII.
-------
MASS BALANCE IN FOUNDS PER PAT
FOR SAMPLE DATE EHBIMO B»0»14 AI 0100 HOURS
FRACTION
METALS
NON-CONV. MEIALB
PARAMETER
CAIIHIUH
CHftONIUfl
COPPER
CVAHIPE
LEAB
MERCURY
NICKEL
IELENIUH
SILVER
THALLIUM
I IMC
ALUMINUM
•ARIUM
IOROM
CALCIUM
IRON
HAOHHIUH
MANOANfBE
SODIUM
TIN
TITANIUM
INFLUENT
3.4
44.4
17. f
1031
47.2
N-D
3»,7
1.9
9.2
1.1
144
1271
43.0
• 1.7
I44lf
•32
3374
79.3
174994
24.2
7.1
TOTAL*
OUT
3.4
71.1
9f.O
I9f
43.4
.3
47. 9
t.l
9.4
.3
142
-
-
-
-
-
-
-
-
-
-
PRIMARY
(FFLUtNt BLUDOC
3.
I,
1.
41.
19.
H-l>
24.
1.
1.
•
40.
227
I«.
47.
,
17.
22.
97.
17.
I
9.
L
1,
.1
N-»
33.1
NOT RUM
NOT RUN
NOT RUN
till* NOT RUN
141 NOT RUN
2343 NOT RUN
90.0 NOT RUN
10B34B NOT RUN
10. 1 NOT RUN
N-fi NOT RUN
SECONDARY
BLUBOE
1.2
90.4
14. t
97.4
10. 4
.2
17.4
.1
2.9
M-B
4B.4
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUN
« FOIAL MASS UUI IB NOI APJU8UO BT MASS CONTAINED IN RETURN FLOWS
POLLUIANIS NOT LISTED WERE NOT DETECTED AT ANT SAMPLE POINT
L-IESE THANI H-D'NOI btTiCTEH.
-------
MASS BALANCE IN POUNDS PER DAT
FOR SANfLC DATE END1NO 800917 AT 0600 HOUfcB
FRACTION
CONVENIIONALS
NON-CONVENTIONALB
VOLAT1LEB
ACID EXTRACT
»ASE-NEUTRALB
PESTICIHEB
HETALB
PARAMETER
»OD
TOTAL SUSP. 8DLIPB
COD
OIL I OREASE
10CAL PHENOLS
TOTAL SOL 108
TOTAL DIBB. BOLIDB
VOLATILE PISS. BOLIDB
TOTAL VOL. BUB. SOLIDS
AMMONIA MITROOEN
TOC
BENZENE
CHLORODENZENE
1, t,1-TRICHLOROETHANE
Ifl-DICHLOROETHANE
CHLOROFORM
1»2-TRANB-DICHLOROETHYLENE
ETHYLBENZEME
METHYLENE CHLORIDE
TE TRACHLOROE THTLENE
TOLUENE
TRICHIORDETHTLEME
2>4i4-TMfCHLOROPHENOL
2H-DICIILOROPHENOL
2i4-DINETHYLPH£NOL
PENTACHLOROPHENOL
PHEMOL
li2i4-TRICHLORO»ENZENE
I>2-DICHLOROBENZENE
1,4-MCHLOROBENZENE
FlUORAHTHENE
NAPHTHALENE
DI8<2*ETHYLHEXVL) PHTHALATC
IUTYL IEN2YL PHTHALATE
DI-N-IUTVL PHTHALATE
D1ETHYL PHTHALATE
DIMETHYL PHTHALATE
1,2-BCHIANTHRACENE
CHRYBENE
ANTHRACENE
PHEHANTHRENE
PYRCNE
AI.PHA-ENKOBULFAN
ALPHA-BHC
ANTIMONY
INFLUENT
83944
98477
243894
22491
103
431020
130840
80348
393B4
9098
34977
4,8
N-D
10.3
N-D
43.0
1.2
11.4
21.4
30.0
49.0
1,8
N-D
,4
N-D
1.2
117
30.0
3.3
1.2
N-D
11,1
9.1
2.4
2.1
2.4
N-D
N-D
N-D
N-D
,9
N-D
.3
1.3
TOTAL9
OUT
192347
1972*1
332844
20833
41.4
389870
383444
97394
144299
3378
27390
,9
L O.I
.9
.2
7.4
L O.I
1.2
9,9
2.0
4,7
2,2
,9
,9
2.4
1,1
11.3
19.2
.3
N-D
.3
1.3
33.0
1.9
1,9
.3
.3
.4
.4
,8
.8
,4
N-D
N-D
EFFLUENT
11290
• 139
37744
788
43.4
319279
300108
78243
4989
3131
13734
.3
N-D
.3
N-D
7,1
N-D
.3
8.1
.8
2.9
N-D
.9
.3
2.4
1.1
11.3
1.8
.3
N-D
N-D
1.3
1.3
,3
,3
.3
.3
N-
N-
N-
N-
H-
N-
N-
PRIHARY
BLUDOE
33320
70893
107937
13927
1.7
94209
4239
2834
48207
30.7
3199
L 0.1
L 0.1
N-D
,2
L 0,1
L 0,1
,8
,2
1.4
.9
2,1
N-D
N-D
N-D
N-D
N-D
11. 1
N-D
N-D
.3
N-D
14.4
1,0
1.2
N-D
N-D
.4
.4
.8
,0
.4
N-D
N-D
BCCONDARY
BLUDBC
107937
HM4t
187123
4118
14.9
174384
77117
14317
113103
394
8437
L 0.1
N-D
N-D
N-D
.4
N-D
,1
1.2
,4
,9
'L o.i
N-
K-
N-
N-
N-
2
N-
N-
N-
N-
17
N-
N-
N-
N-
N-
M-
N-
N-
N-
N-
N-
3
3
12.4
2,9
1.8
.3
.8
• TOTAL MASS OUT IB NOT ADJUSTED DY MASS CONTAINED IN RETURN FLOH8
FOILUTANTB HOT LISTED WEKE HOI DETECTED AT ANY SAMPLE POINT
L-LEB9 THANI N-ti-NOI DETECTED,
-------
HA8B VALANCE IH POUNDS UK PAY
FOR SAMPLE DAT! ENDINO flOO»17 AT 0800 HOURS
FKACIION
METALS
MOM-COMV. METALS
7
.p-
PARAHCTER
ARSENIC
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
NICKEL
SELENIUM
SILVER
THALLIUM
ZINC
ALUMINUM
•ARIUH
DOROM
CALCIUM
IRON
MAGNESIUM
HANOANCSE
SODIUM
TIN
TITANIUM
INFLUENT
I.B
2.7
lit
1B.1
MSI
24.
79.
1.
9.
*
122
I17f
43,4
44. •
I22f9
709
21**
43. 1
100297
If. 9
4.S
TOTAL*
OUT
I.S
1.4
71. t
24.*
141
27.0
19.4
.9
4.1
.9
H2
-
-
-
-
-
•*
-
-
-
-
EFFLUENT
.1
1.1
• .7
N-D
20.9
M-D
24,4
.9
.9
,1
30.9
PRIMARY
SLUDOE
.1
L 0,1
4.0
10.9
41.4
22.7
7.4
N-S
.4
N-D
21.1
SECONDARY
ILUDQE
,7
N-S
41.2
14.4
SO. 4
4. a
1.4
M-0
9.0
M-0
101
342
7.4
1*0
S443
110
ISIS
II,•
14140
11.0
N-t
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
HOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
MOT RUN
NOT RUM
NOT RUN
NOT RUM
« IOTAL MASS OUT IS HOI ADJUSTED SY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS HOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-LESB THANI N-D-HOI DETECTED.
-------
FRACTION
CONVENTIONALS
MASS RETURNED TO PLANT IN POUNDS PER I'AY
FOR SAMPLE DATES ENDINO 60/09/17 AND 80/0V/18 AT 0800 HOURS
PARAMETER
NUN-CONVENTIONAL8
VOI.ATILES
DDK
TOTAL 8U8P. BOLIPS
COD
OIL I OREASE
TOTAL PHENOL•
TOTAL SOLIfS
TOTAL 11181. BOLItB
TOTAL VOLATILE 80LID8
VOLATILE tllSB. 80LID8
TOTAL VOL. 809, SOLIDS
AMMONIA HITROOEN
fOC
»ENZCNE
CIILORTIDENZENE
CMLOROETHANE
1>2-TRAN8-DICHLOROETHVLENE
EIHTLDENZENE
HETHTLENE CHLORIDE
TOLUENE
VIHTL CHLORIDE
2i4»4-TRICHLOROPHENOL
2i4-DlCHLOROPHENOL
PENTACHLOROPHENOL
PHENOL
1«2<4-TRICHLDRODENZENE
li2-DICHLOKO>ENZENE
!>4-DtCHLORODEHZENE
FLUORANTHENE
NAPHTHALENE
DIBI2-ETHVLHEXVLI PHTHALATC
DUTTL DENZTL PHTHALATE
DI-N-DUTVL PHIHALATE
ni-N-DCTTL PHTNALATE
DIETHYL PHTHALATE
PHENANTHRENE
PYRENE
ENDRIN ALDEHYDE
CCLfA-DHC
ANTIMONY
ARSENIC
•ERYLL1UM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-IC89 TMANl H-ti-NOI DETECTED,
ACID EXtRACT
BASE-NEUTRALE
PlBTtCIDES
METALS
DIOESTEfi VACUUM FILTER
SUPERNATANT FILTRATE
424? 20.7
178? 19.2
•4*3 93. 0
423 .7
.1 L 0.
4101 ISO
20m 242
3083 191
303 4*. 7
2324 14.0
40.0 12.7
400 29.0
L 0. N-0
I 0. M-fr
L 0. N-0
I 0. N-D
L 0. H-D
L 0. N-D
L 0. L 0.
L 0. M-D
N-D L 0.
L 0.1 L 0.
N-D L 0.
.1 L 0,
.4 L 0.
L 0.
L 0.
L 0.
.1
t 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L o.
L 0.
L 0.
.2
L 0.
I 0.
L 0.
N-0
H-D
L 0.
L 0.
N-D
L 0.
N-D
L 0.
N-D
N-0
N-D
N-D
L 0.
L 0.
N-D
L 0.
2.1 L 0.
2.2 L 0.
NOI DUN .7
1.7 L 0.
1
1
1
1
1
1
1
1
1
1
1
1
1
TOTAL MASS
RETURNED
4241
3B22
B7it
424
,3
4431
20441
323f
979
2940
32,7
423
L
L
L
L
I
L
L
L
L
L
L
l>
,
L
L
L
»
L
L
L
L
L
L
L
L
L
L
,
L
L
2.
•
•
•
,
•
f
.
•
•
*
•
*
•
•
•
.
•
.
•
*
•
•
•
t
,
•
2.2
-
1.8
-------
TRACIION
HE] All
MASS RETURNED TO PLANT IN POUNDS PIR DAT
fOK SAMPLE DATES ENPINO SO/OV/17 AND SO/Ot/IS AT OSOO HOURS
PARAMETER
NON-CUNV. METALS
MERCURT
NICKEL
SELENIUM
SI I. WE*
THALLIUM
ZINC
ALUMINUM
SARIUN
KORON
CALCIUM
COBALT
IRON
HAOHESIUH
NANOANEBE
HOLVDDENUH
SODIUM
TIN
TITANIUM
VANADIUM
TTTRIUM
DIOI
SUP)
L
•
L
.
L
4.
77.
2.
,
4f?
,
93.
94.
3.
,
2B2
L
.
•SfER VACI
:RNATANT FIL
.1 N-D
L
.1 L
L
.1 L
L
t
L
L
27.
N-D
,
».
L
N-D
it.
L
L
.1 H-D
1 L 1
MM
[Rl
,
.
.
*
•
.
.
.1
,
.
>.
1 FILTER TOI4
kTE RCTI
L
1
I
9
L
7.
77.
2.
1
323
•
3.4.
43.
3.
•
J4f
1
1
L
1
kL HASB
IRKED
.1
.1
.1
.1
rOLLUTANII NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
L>LE88 THAN! N-D>-HOr DETECTED.
-------
HASB fiALAHCE IN POUNDS PER DAY
FOR SAMPLE DATE END1NO 800*10 AT 0800 HOURS
FRACTION
CONVENTIONAL8
NOM-CONVENTIONAL8
UOLATILEB
ACID EXTRACT
BASE-NEUTRALS
PESTICIDES
ftCTALS
PARAMETER
POP
TOTAL SUSP. SOLIPS
COD
OIL I OREA8E
TOTAL PHENOLS
TOTAL BOLIPB
TOTAL PIBB. BOLIPS
TOTAL VOLATILE 80LIDB
VOLATILE DI88. SOLIDS
TOTAL VOL, SOB. SOLIDS
AMMONIA NITROOEN
TOC
BENZENE
CHLOROVENZENE
I.I>I-TRICHLOROETHANE
l»t-DICIILORO£THAHe
CHIOROFORH
1,2-TRANB-DICHLOROETHVLENE
ETHYLDENZENE
NETHYLENE CHLORIDE
TR1CIILOROFLUOROME THANE
PICHLORODlFLt/OROMCTHANE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2>4«4-TRICHLOROPHEHOL
2.4-DICHLOROPHENOL
PENTACHLOROPHENOL
PHENOL
ACEHAPHTHENE
Ir2,4-TRICHLQRO»EHZEHE
1.2-DICHLOROBENZENE
I>3-DICHLOROBENZEHE
1i4-DICHLOROBENZENE
FLUORAHTHENE
NAPHTHALENE
»ISI2-EIHYLMEXVL) PHTHALATE
PUtn BENZYL PHTHALATE
OI-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
PMEttANTHRENE
PYREHE
OAMMA-BHC
AMI1HDNY
ARSENIC
INFLUENT
2IH19
H»74»
308963
97f43
235
438141
442019
1*140*
81043
•1783
743f
*3*42
10. A
.8
94.8
1.2
4*. I
.8
3.1
21.9
N-D
H-f
20.0
NOT RUM
3.1
N-P
.8
2.3
144
N-P
29.4
3.*
N-P
2.3
N-P
47.0
7.
1.
2.
1.
1,
N-P
M-P
1.4
2.3
TOTAL*
OUT
2083*4
202173
414837
-
40.3
4*2910
91172*
2377*8
123847
1421*4
9149
43444
1.3
.2
.7
.2
7,3
L 0.1
.8
9.1
L 0.1
.9
2.4
78.4
1.3
I.I
I.I
2.9
24.*
2.9
10.8
.'7
.9
.4
.9
10.0
30.*
H-P
I.I
.7
N-P
.4
.3
3.2
2.4
EFFLUENT
19*3*
18044
*9432
NOT RUN
92.4
4941**
4304*7
108383
74380
123*7
4404
2018*
t.l
N-P
.7
H-P
4.7
N-P
H-P
4.4
H-P
H-P
.7
43.8
H-P
I.I
I.I
2.9
24.*
2.9
9.7
.7
N-P
H-P
H-P
8.9
8.9
N-P
1.1
.7
N-P
N-D
.3
2.1
1.4
PRIMARY
SLUPOC
41317
94292
1032*1
149*3
1.4
73984
***4
42418
4840
39083
21.3
1844
.1
L 0.1
H-P
.2
L 0.1
L 0.1
.4
.2
L 0.1
N-P
1.3
8.2
1.2
H-P
H-0
N-P
H-P
N-P
S.I
N-P
.3
.4
.3
1.9
8.7
N-P
H-D
N-D
N-D
.4
N-D
.2
.2
8ECONPART
8LUDOE
191140
127837
219*14
323*
14,9
142727
71034
847*7
42407
V47I4
940
213*1
.1
L 0.1
H-D
H-P
.9
N-P
.2
.3
H-P
.9
.4
4.4
L 0.1
N-P
N-P
H-P
H-D
H-D
H-P
H-D
H-P
H-P
N-D
H-D
13.3
N-P
«-D
N-D
H-D
N-D
M-D
.*
.8
* TOTAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTEH WERE NOT DETECTED AT ANY SAHPLE POINT
L-LES3 TMANI N-tl-NOr HETtCIED.
-------
MASS VALANCE IN POUNDS PER DAY
FOR SAMPLE DATE ENDIMO SOOflB At 0100 HOURS
FRACTION
NET ALB
7
00
HOM-COMV. METALS
PARAMETER
•ERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SELENIUM
SILVER
IHALLIUH
ZINC
ALUMINUM
DAKIUN
DORON
CALCIUM
IRON
MAONEBIUH
HAHOANESE
SODIUM
UN
TITANIUM
VANADIUM
VTTRIUH
INFLUENT
TOTAL*
OUT
N-D
1.9
IJ»
*4.2
117*
37.2
.a
13.4
.•
12.a
.4
287
1231
M.7
74.1
ItOOt
2093
1M3
St.7
U32I7
2*. 4
27.4
1.2
2.0
1.2
2.2
as.4
22.3
211
80.0
.2
12.1
1.4
4.1
.4
IBS
IFFLUCNI
N-D
2.1
24.4
2.S
Si. 7
11. f
N-D
27.4
1.4
.7
.4
14.7
PRIMARY
•LUDOt
N-»
L 0.1
*.7
12. »
to.s
12.1
.2
l.t
N-»
.9
H-D
**.*
SECONDARY
SLUDOE
1.2
N-P
27.1
4.B
f3.4
3.1
H-D
2.B
.2
4.7
N-D
S2.B
411
12.1
««.
1UBS
201
247f
]»
-------
FRACTION
CONVEHTIONALS
NON-CONUENMONALB
VOLATILEB
VO
HASS BALANCE IN FOUNDS f£R DAY
FOR SAMPLE PATE ENPINO 800919 AT 0800 HOURS
PARAMETER
BOD
TOTAL SUSP. SOLIDS
COD
OIL I OREA8E
TOIAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
VOLATILE DIBS, SOLIDS
TOTAL VOL. SUS. SOLIDS
AHNONIA MIIROOEN
TOC
DENZENE
CHLOROtENZENE
Itld-TRICHLOROETHANE
I.I-DICHLOROETHANE
CHLOROFORM
1 > 2-TRANS-DICHI.OROETHYLEHE
ETHYLBEHZENE
HETHVLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2r4-DICHLOROPHENOL
FENTACHLOROPHEHOL
PHENOL
1,2,4-TRICHLOROHENZEME
I>2-DICHLOROBENZENE
li3-DICHLORO»ENZENE
Ir 4-DICHLDROBEMZEHE
FLUORANTHEHE
NAPHTHALENE
BIS(2-ETIIYLHEXVL> PHTHALATE
BUTYL BENZYL PHTHALAIE
DI-N-1UTYL PHTHALATE
METHYL PIIIHALATE
1>2-BENZANTHRACENE
CHRYSENE
AHTHRACEHE
FHENANTHRENE
PYRENE
OAMNA-DHC
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
* TOTAL HASS OUT IB NOT ADJUSTED *Y MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED WIRE NOT DETECTED AT ANY SANPLE POINT
THANI H-D-NOT DETECTED.
ACID EXTRACT
BABE-NEUTRALS
PESTICIDES
METALS
INFLUENT
183924
16937*
439824
3277?
439
B2I27I
443414
112799
94342
8794
59974
4,4
H-0
3.2
H-D
14.4
.4
2.4
23.2
14.8
74.0
1.2
.4
2.8
288
44.0
4.8
N-D
3.4
N-P
40.0
4.0
.a
1.4
2.0
H-D
N-D
H-0
1.2
N-D
.8
1.4
7,2
.4
4.0
TOTAL*
OUT
2 13 408
249704
438438
19984
fl.7
743432
993120
143843
189433
4883
39220
.8
L 0,1
.7
L .1
19.
L .1
.
3.
I.
17.7
,5
.4
N-0
B.»
4.1
N-D
.2
.2
,2
S.I
19,7
.8
1.4
2.2
.2
.2
2.S
3.2
.2
H-D
.9
2.3
N-D
2.5
EFFLUENT
21751
19214
101904
1450
74.1
487994
444390
10474*
14SOI
4350
21024
,7
N-D
.7
N-D
14.3
N-D
N-D
2,9
•1.1
13.4
N-D
,4
N-D
.4
1,1
N-D
N-D
N-0
N-D
I.I
2,5
N-D
.7
2,2
N-D
N-D
N-D
.7
N-D
N-D
.4
1.5
N-D
2.5
PRIMARY
SLUDGE
33320
39984
104424
9994
3.1
58318
4054
849
24943
29.3
1399
N-D
L O.I
N-D
L O.I
L 0.1
L 0.1
,3
L 0,1
.1
,9
.3
H-D
N-D
1.2
3.2
N-D
.2
.2
.2
2,1
3,4
.8
.7
N-D
.2
.2
.8
.8
.2
N-D
.1
.2
N-D
N-D
SECONDARY
SLUDGE
158337
190508
230308
4138
12.3
199340
84474
38223
148189
904
I2S9S
L O.I
N-D
N-P
N-D
.4
H-D
.2
N-D
,4
3.4
N-D
H-D
H-D
7.3
H-D
N-D
N-D
H-D
H-D
2.1
7.4
H-D
N-D
N-D
N-D
N-D
1.7
1.7
N-D
N-D
.4
.8
H-D
N-D
-------
HA88 8ALAHCE IM POUNK8 PER PAT
FOR 8AHPLE DATE ENPINO lOOflf AT OROO HOUKI
FRACTION
METAL8
MOM-CONV. HETALI
PARAMETER
CHROMIUM .
COFFER
CYANIDE
IEAD
HERCURT
NICKEL
SELENIUM
SILVER
tHALLIUH
ZINC
ALUMINUM
•AMIUH
•ORON
CALCIUM
COPALT
IRON
MAONEDIUH
MANOANEIE
HOLYfPEHUH
IOPIUH
TIN
UTANIUH
VANADIUM
YTTRIUM
INFLUENT
TOTAL*
OUT
1107
13.4
N-D
49.3
.»
f.4
.4
ZIO
73.1
24.3
211
4f.
301
2.
7.
.4
211
•9.2
71,2
aaiti
14.1
47f»
If. 4
14.4
U4IJ4
21.2
42.4
4.4
3.4
EffLUIHT
20.1
4.4
37.7
24. •
N-D
21. t
l.t
1.9
.4
27. f
410
11.0
t4.4
12411
1».4
22».'
1»00
>»•?.
N-»
190444
23.4
1.1
N-B
N-0
fRIHARr
•LUBOE
2.4
4.0
S».7
17.9
N-D
1.4
N-D
.4
N-D
32.0
NOT RUN
HOT HUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
•ECONDARV
ILUDAE
90.4
19.1
133
29.2
.3
9.4
.2
3.i
N-D
191
NOT RUN
HOT RUN
HOT RUH
HOT RUH
NOT RUN
HOT RUN
HOT RUH
HOT RUN
NOT RUH
NOT RUN
NOT RUH
HOT RUH
HOT RUH
NOT RUH
« TOTAL MASS OUT 18 NOT AHJU8IED >V HA88 COHTAIHED IN RETURN FLOW*
POLLUTANTS NUT LlBTEIi UERE HOT DETECTED AT ANY 8AHPLE POINT
L-LEB8 THAN! H-D-NOT MHCTED.
-------
MASS BALANCE IN FOUNDS PER DAT
FOR SAMPLE DATE EMUINO 800*20 AT OBOO HOURS
FRACtlON
CONVENTIONAL8
NON-CONVENT10NAL8
VOLAT1LES
PARAMETER
•OP
TOTAL SUSP, SOLIDS
COD
OIL I OREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DISS. SOLIDS
TOTAL VOLATILE SOL ITS
VOLATILE DISS. SOLIDS
IOTAL VOL. SUB. SOLIDS
AMMONIA NITROOEN
TOC
ICNZENE
CHLORODENZENE
IiIrI-TRICHLOROETHANE
CHLOROFORM
11 Z-TRANS-OICHLOROETHITLEME
ETHVLtEMZEMC
HETHYLENE CHLORIDE
TETRACHLOROETHVLENE
TOLUENE
TRICHLOROETHYLENE
2.4. 4-TRICHLOROPHENOL
2 • 4 - DICIIL OROPHENOL
PENTACHLOROPHENOL
PHENOL
ACENAPHTHENE
IF 2.4-TRICHLOROIENZENE
I>2-DICIUORO»EMZENE
l>3-DICHLOROBEHZENe
1>4-DICHLOROSENZENE
FLUORANTIIENE
NAPHTHALENE
lttt<2-ETHYLHEXYL> PHTHALATE
>UTVl ICHZYL PHTHALATE
DI-N-SUTYL PHTHALATE
DIETHYL PHTHALATE
ANTHRACENE
PHENANTHRENE
fYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
I TOTAL MASS OUT IS NOT ADJUSTED DY MASS CONTAINED IN RETURN
POIIUTANTS HOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L'lEBS THAN* N-li-NOT DETECTED.
ACID EXTRACT
SASE-NEUIRALS
METALS
INFLUENT
133*38
12444*
283387
21341
474
17*248
242IOJ
»4442
2833*
82217
8047
48*80
i.a
,7
3.5
4,4
1.0
13. 4
2.1
3*. s •
1»»
II. 9
1.0
.7
3.1
238
N-D
18.2
1.4
.7
1.0
N-D
13,4
3.2
,7
1.0
3.3
N-D
.7
N-D
2.8
4.2
N-D
3.3
43,9
43.7
TOTAL*
OUT
1743*3
224843
344708
14311
If*
41472*
414443
202122
1017*4
148330
4*3*
3*4*2
.4
L 0.1
N-D
4.*
•a i
1.1
1.4
1.7
13.1
.4
.4
N-D
1.3
4.7
.4
7.0
N-D
N-D
.3
.3
3.7
14.2
I.I
1.3
.3
.7
.7
.3
2.4
3.2
3.1
1.4
44.4
32.4
EFFLUENT
171*0
13732
71883
1230
174
37234*
321*18
4*364
37308
11231
4374
13002
.3
H-D
N-D
4,7
N-D
.4
1.4
.*
10,*
N-D
,4
N-D
1.3
4.7
,4
3.1
N-D
N-D
N-D
N-D
1,3
.4
N-D
,3
.3
N-D
N-D
N-D
1.4
1.*
N-D
1.4
12.3
4.3
PRIMARY
SLUDOE
22438
33*78
73304
7844
3.4
4T*33
43*7
34223
3732
30434
42.4
Iff*
N-D
L O.I -
N-D
N-D
,2
.3
L 0,1
H-D
.7
L Oil
N-D
N-D
N-0
N-D
N-D
3.*
H-D
N-D
.3
.3
2.4
• •I
1.1
t.O
N-D
.7
.7
.3
L 0.1
,4
,4
N-D
8,0
II.*
SECONDARY
BLUDOE
134743
I37II3
20131*
71*7
l*.3
172227
84130
*4SI3
40334
104443
340
224*1
L 0,1
H-D
N-D
,2
N-D
.2
N-D
,8
1,3
,3
H-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-0
N-D
7.3
N-D
N-D
N-D
N-D
H-D
N-D
,*
.*
2.7
N-D
23.*
14.4
-------
NABS BALANCE IN POUNDS PER PAT
FOR SAMPLE HATE ENDINO 800120 AT 0000 HOURS
FRACTION
METALS
NOM-COHW. METALS
PARAMETER
CYANIDE
IEAD
MERCURY
NICKEL
SELENIUM
SILVER
THALLIUM
ZINC
ALUMINUM
BARIUM
DORON
CALCIUM
COBALT
IRON
HAONEBIUM
MANGANESE
MOLYBDENUM
SODIUM
TIN
TITANIUM
VANADIUM
YTTRIUM
INFLUENT
TOTAL*
OUT
2*32
93.2
N-D
4».0
1,0
B.O
.1
144
2492
92.9
101
I44f4
20.1
1330
2799
111
13.3
aim
24.1
U.I
2.0
1.7
70. *
.3
43.9
,B
• .4
.«
218
EFfLUENT
22.9
23.3
N-B
32.2
.A
.4
,t
2B.1
PRIMARY
•LUDOe
S2.S
18.7
N-D
l.t
N-0
1.3
N-P
30.7
SECONDARY
•LUDOE
T2.B
24.4
,3
».4
.2
4.3
N-D
131
27*
10.4
4ft.4
11344
N-D
174
2900
14.7
N-D
111977
24.4
N-D
N-D
N-D
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
I TOTAL MASS OUT IS NOT ADJUSTED DY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
L'LESS THAN! H-D'NOI DETECTED.
-------
FRACTION
CONVENTIOHAL8
NOH-CONVENTIONAL8
PARAMETER
•OD
TOTAL SUSP
COD
OIL I OREABE
MASS BALANCE IN POUNDS PER PAY
FOR SAMPLE DATE ENDINO 800921 AT OBOO HOURS
SOLIDS
TOTAL PHEHOLS
TOTAL SOLIDS
TOTAL DISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMHOHIA NITROOEH
TOC
VOLATILES BENZENE
CHLOROSENZENE
1,1>1-TRICHLOROETHANC
1,1-DICHLOROETMANE
CHLOROFORH
I.2-TRAH8-OICHLOROETHYLEHE
ETHYLPEHZEMC
HETHYLEHE CHLORIDE
TETRACHLOROETHYLENE
TOLUEHE
TRICHLOROETHYLENE
AC I IP EXTRACT 2t4.4-TRICHLOROPHENOL
2.4-DICHLOROPHEMOL
PENTACHLOROPHEHOL
PHENOL
DASE-NEUTRALS ACEHAPHTHEHE
11214-TRICHLORODEHZENE
lt2-DICHLDROBENZENE
l>4-PlCHLOROtENZENE
FLUORANTHENE
NAPHTHALENE
flB(2-ETHYLHEXYL) PHTHALATE
BUTYL DENZYL PHTHALATE
DI-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
ANTHRACENE
PHENANTHREHE
PYRENE
PEST 1C UiEB ALPHA-ENHOSULFAN
HITALB ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
I TOTAL MASS OUT IS NOT ADJUSTED BY MASS COHTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED UEkF NOT DETECTED AT ANY SAMPLE POINT
L-l ES3 TMANI N-t^HOI DETECTED.
INFLUENT
101709
75203
20341*
12328
248
30204*
319747
94142
32»7B
34841
4781
40047
1,8
.4
13.9
N-D
a. a
.4
HO! RUN
2.1
to.8
211
i.e
.9
H-D
2.2
ao.i
M-D
20.0
.3
.4
.3
4,2
4,4
.V
1.2
1.2
M-D
1.3
.4
.a
1.2
I.S
M-D
3.1
TOTAL*
OUT
114127
193744
241413
17191
37,7
43354V
348249
140310
74338
142019
3213
33429
,4
H-D
*
1
3.
*
1*
ti
,
A.
•
»
t
t
i,
,3
5,4
N-0
.2
.2
3.3
17,3
.9
.9
.3
.3
.3
,3
H-D
3.3
3.1
.3
2.0
EFFLUENT
10834
3147
40434
N-D
28.7
240592
183444
40092
23735
4334
2709
• 939
.3
N-D
,3
N-D
3,1
N-D
,8
1.4
,3
4.1
.3
.3
,3
,8
1.4
.3
2.4
N-D
N-D
H-D
2.7
.3
N-D
.3
.3
N-D
N-D
N-D
H-D
2.2
1.1
N-D
1,9
PRIMARY
8LUDDC
33330
41189
42442
9994
1,4
34440
2222
29013
434
23331
34.0
1999
N-D
M-D
N-D
.1
N-D
.2
.2
L O.I
N-D
.4
N-D
N-D
N-D
N-D
N-D
N-D
2.0
N-D
.2
.2
.8
4.9
.9
.4
N-D
.3
,3
.3
H-D
L O.I
.2
.3
.1
SECONDARY
•LUDOE
71971
148738
158337
7197
7,4
138337
42343
91401
47949
11SI34
448
32491
.1
N-D
N-D
N-D
.1
N-D
,2
N-D
,3
1,3
L O.t
N-D
H-D
N-P
N-D
N-0
1.2
N-D
N-D
H-D
H-D
11.9
H-D
N-D
H-D
N-D
N-D
N-D
H-D
1.0
.8
N-D
N-D
-------
MIS BALANCE IN POUNDS PER DAY
FOR SAMPLE DATE EMBINO BOO»2I AT OBOO HOURB
FRACTION
HE1ALB
NON-COMV. METALS
PARAMETER
CHROMIUM
COPPER
CYANIDE
LEAK
MERCURY
NICKEL
HELEN I UN
SILVER
THALLIUM
ZINC
ALUMINUM
BARIUM
BORON
CAICIUM
COBALT
IRON
MAONEBIUH
HAHOANEBC
SODIUM
1IN
IITANIUH
VANADIUM
INFLUENT
12.4
2? .»
1424
49.4
M-ft
».4
.4
«.»
.1
I2»
ion
OU1
5f.
27.
lit
74.
B
27.
*
B.
,
237
11.*
1
EFFLUENT
PRIMARY
BLUBOE
SECONBARY
ILUBOE
14.•
74.4
11712
N-D
487
2444
40.1
7242?
If.I.
4.9
4.2
4
3f
24
H-tl
21
27,
7.
3f .
Ill 7
22.
»a.
2147
40. f
471BI
17. J
N-D
.3
4.0
• .9
86.4
10.•
N-B
I.J
N-B
l.f
N-B
Si.l
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
44.B
il.7
• f.2
If.4
.]
3.4
.4
4.9
N-B
174
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
4 IOFAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOWS
PULLUIANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
I.-LE6S THAN I N-D-NOI DETECTED.
-------
NASS DALANCE IN POUNDS PER DAY
FOR SAMPLE DATE ENDINO 810211 AT 0800 HOURS
FRACTION
CONVENT IONALS
NON-CONVCHTIONALB
VOLATILE8
PARANEIER
HOD
TOTAL SUSP. SOLIDS
COD
OIL I OREABE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE KISS. SOLIDS
TOTAL VOL. BUS, SOLIDS
AMMONIA NITROGEN
TOC
DENZENE
lilM-TRICHLOROETHANE
CHLOROFORM
ETMYl BENZENE
NETMYLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHTLENE
2i4-DICHLORDPHENOL
PENTACHLOROPHENOL
PHENOL
ACEHAPHIHENE
li2»4-TRICHLOROBENZENE
t»3-DICHLORODENZENE
FLUORANTHEHE
NAPHTHALENE
BISO-ETHTLHEXYL) PHTHALATE
BUTYL DEHZYL PHTHALATE
DI-H-DUTVL PHTHALAU
DIETHYL PHTHALATE
!>2-DENZANTHRACENE
IENZO (AIPYRENE
1 1 « 12-BENZOFLUORAHTHEHE
CHRY8ENE
ANTHRACENE
FLUORENE
PIIENANTHRENE
PYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COFFER
I TOTAL MABB OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS HOT LISTED WERE HOT DETECTED AT ANY SAMPLE POINT
L-I.E9S TH*NI N-P-NOT DETECTED,
ACID EXTRACT
BASE-HEUTKALS
Htm 6
INFLUENT
64739
383*9
117*24
4433
12*
262017
303421
86233
S1S91
34641
1474
68176
6.6
H-D
IS. 4
H-D
162
8.1
Sf.O
2.2
1.1
4.1
II. 1
H-D
H-D
.4
H-D
4.1
S.3
N-D
N-D
N-D
N-D
N-D
H-D
N-D
H-D
N-D
H-D
H-D
H-D
N-D
H-D
H-D
103
40.9
TOTAL*
OUT
100086
2087SO
393458
1*33*
30.2
468332
23*648
1*2383
42*80
14*404
I2VB
60144
2.0
.1
20.8
L O.I
• .0
1.8
4.2
.1
.7
9.4
34.7
,7
1.7
H-D
.3
1.2
2.9
.3
1.0
1.0
.3
.8
.2
.3
L O.I
L 0.1
.2
.2
L O.I
3.1
1.1
3.1
477
8*. 8
EFFLUENT
*306
3630
3317*
2327
24.3
246*49
2412*8
42211
378*0
4321
»»7
18413
2.0
H-9
!»,»
H-V
8.0
1.0
4.0
M-0
.7
N-D
94. 3
.7
H-
N-
N-
M-
2
N-
1
1
H-
H-
H-
H-
H-
H-D
H-D
N-D
H-D
H-D
H-D
H-D
23.3
10.6
PRIMARY
SLUDOC
8013
623*
1840*
2438
.3
4*09
443
4072
412
3440
13.0
1949
H-D
L 0,1
I O.t
L O.I
N-D
L 0.1
.2
L 0.1
N-D
N-D
.2
N-D
.2
N-D
.3
,2
.9
.3
N-D
N-D
.3
.8
.2
.3
L 0.1
L O.I
.2
.2
L 0,1
.2
L O.I
.2
21.7
4,0
SECONDARY
BLUDOE
82767
1*6841
323870
14374
3.4
214474
17705
146102
4478
141423
288
3*384
M-D
,1
,8
' N-D
H-D
.7
H-D
,1
H-D
3,4
H-D
M-D
1.3
H-D
H-D
1.0
H-D
H-D
N-D
H-D
N-D
H-D
K-D
N-D
N-D
N-D
N-CI
N-D
N-D
J.»
I.I
2.9
432
43.2
-------
HASH MLANCE IN POUNDS UK DAT
FOR SAHPLE DATE IHPIHO 11021I AT 0100 HOUKI
FRACTION
HETALI
NON-CONV. nETALI
PARAHETER
CYANIDE
LEAD
HEKCURV
NICKEL
•ILVER
ZINC
ALUHINUn
MRIUH
•OROH
CAtCIUH
COtALT
IRON
ItAOMESIUH
NANOANESE
•OI> I UN
VANADIUM
INFLUENT
TOIAL*
OUT
10.0
19.7
.2
N-0
2.2
30*
1729
II.0
11.1
14004
4.4
1*77
2211
77.4
41B34
2.*
17.7
14.0
L O.I
92.7
• .»
20*
CFFLUENI
14.4
N-0
N-D
28. »
.1
!».»
PRII
•LUI
•
2.
t
2.
•
20.
IARV IECONDARY
IOE ILUDOE
.9
I J.I
.1 N-»
20, f
7.4
140
121
7.0
29.4
112*9
1.0
121
Iff 4
41.1
48119
M-0
HOI ftUN
HOI RUN
HOT RUN
NOt RUM
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOI RUN
HOT RUN
I TOTAL HA8S OUT 18 NUT AVJU8TEP »T NABS CONTAINED IN RETURN FLOUB
POLLUTANTS HOT LISIEII UERE NOT DETECTED AT ANY 8AHPIE POINT
L-LES6 THAN I N-D-MOI DEUCIEH.
-------
FRACTION
CONVENTIONALS
MON-CONVENUONALB
UOLATILE8
MASS BALANCE IN POUNDS PER DAY
FOR BAtlFLE DATE ENDlND 810212 AT 0800 HOURS
PARAMETER
»OD
TOTAL SUSP. SOLIDS
COD
OIL I OREA8E
TOTAL PHENOLB
TOTAL BOLIDS
TOTAL DIBS. SOL ITS
TOTAL VOLATILE BOLIDB
VOLATILE DIBS. BOLIDS
TOTAL VOL, BUB. BOLIDB
AHHONIA NITROOEH
TOC
UEMZENE
CHLORODENZENE
Iflrl-TRICHLOROETHANE
CHLOROFORM
ETHYLtENZEME
HETMYLENC CHLORIDE
TtTRACHLOROETHYLENE
TOLUENE
IRICIILOROETHYLENE
2t 4-DICHLOROPHENOL
PHENOL
1.3-DICMLOROBEHZEME
FLUORANTHENE
NAPHTHALENE
DIETHYL PIITHALATE
DIMETHYL fHTHALATE
I*2-DENZANTHRACENE
•ENZO (AIPYREHE
11112-DENfOFLUORANTMENE
CHRYBENE
ACENAPHTHYLENE
ANTHRACENE
FLUORCNt
FltENANTHRENE
fTRINE
ANTINOMY
ARSENIC
BERYLLIUM
CADMIUM
CHROHIIIH
COPPER
CYANIDE
IE AD
MERCURY
« TOTAL MASS OUT IB NOT ADJUSTED BY HABB CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS TMANI N-I>'NOT ['EJECTED.
ACID EXTRACT
DASE-NEUTRALB
NETALS
INFLUENT
74B8B
93440
131942
12*4*
1*4
322V28
247488
»9*07
61310
341*7
2426
44771
0.1
N-D
M-D
23,9
N-0
f7.l
S.3
M-D
1.6
2.0
11.3
.8
N-D
6.1
3.6
N-
>-
N-
N-
N-
N-
M-
N-
N-D
N-D
M-D
N-0
N-D
N-D
30.4
34.4
10.9
N~D
M-D
HUM.*
OUT
llf7IT
26614V
111976
18104
f.4
908172
241*1*
219221
2?t98
18929*
923
8SS77
1.1
L 0,1
L 0.1
23.3
.1
12.8
.4
L 0,1
I O.I
1.1
.7
M-D
.3
M-D
7.4
3.7
,2
.1
.2
.2
L O.I
L 0,1
L O.I
.2
.3
.8
4,0
1.1
2.7
28V
46.1
19.3
26.7
L O.I
EFFLUENT
7344
7732
JI2T4
1473
7.4
22*380
221448
101*1
24300
98*1
368
14727
1.1
M-»
N-D
22.9
N-D
32.«
.4
N-D
N-D
l.t
.7
M-D
N-g
M-D
7,4
3,7
M-D
M-D
M-D
M-D
N-P
N-D
M-D
H-D
M-D
N-D
N-0
M-D
N-D
14,6
6.4
7.4
N-D
N-D
PR I HART
8LUDUE
7»»7
183*3
I9**4
3172
.4
I8*2«
948
10042
240
101*4
10.7
1264
L
L
L
I
L
L
L
L
L 0
N-D
H-D
N-D
,1
M-D
N-D
N-D
.2
.1
.2
.2
L O.I
L 0.1
L O.I
.2
,3
L O.I
.4
,1
,2
13.3
7.3
.2
4,4
L 0,1
SECONDARY
BLUDOC
104398
240024
284284
1349*
1.8
29*814
1*720
174170
93*8
148772
144
3*984
N-D
M-D
M-P
.7
.1
N-D
.2
M-D
N-D
N-D
N-D
N-D
M-D
N-D
N-D
N-D
N-D
N-D
M-D
N-D
N-D
N-D
N-D
N-D
N-D
.7
3,4
1.0
2.9
299
J2.4
7.*
22.3
N-D
-------
HAS6 MLANCE IN PQUNMS «R tiM
FOR SAMPLE HATE ENDING 110212 Af 0800 HOUR I
FRACTION
METALS
HON-CONV. ME1ALB
PAftANEIER
NICKEL
BUVER
ZINC
ALUMINUM
•ARIUM
IORON
CALCIUM
COMLT
IRON
HAONESIUH
HANOAMESE
lOlitUH
TITANIUM
VANADIUM
IHFLUENI
TOTAL*
OUT
74.?
1.2
198
134*
24.1
24.7
17104
2.4
1214
2111
101
40701
M-0
2.0
21.7
4.2
171
EFFLUENT
M-»
.4
29.0
PR I HAM
ILUDOE
4.4
.4
24.0
SECOMHAkT
ILUPOE
17. 1
9.4
122
142
•a
17*7
I9B12
2,2
122
44.3
ST444
11.1
H-B
NOT RUN
HOT DUN
MOT RUN
NOT RUM
NOT RUN
HOT RUH
NOT RUN
HOT RUH
HOT RUH
NOT RUH
HOT RUH
HOT RUN
NOT RUH
HOT RUH
HOT RUN
HOT RUH
HOT RUN
NOT RUN
HOT RUH
NOT RUH
HOT RUN
NOT RUN
00
t TOTAL MASS OUT 18 NOT AtiJUSIED M MASS CONTAINED IH RETURN FLOWS
POLLUTANTS NOT LISIEft WERE NOT DETECTED AT ANT SAMPLE POINT
L-LEBS THANI N-b-NO! I'EUCTEU.
-------
MASS RETURNED TO PLANT IN POUNDS PER DAT
FOR SAMPLE HATE END1NO 810212 AT 0100 HOUR!
FRACTION
CONVENTIONAL!
NON-CONVENTIONALB
VOLATILES
VO
ACID EXTRACT
IABE-NEUTMLB
PARAMETER
too
TOTAL SUSP. SOLIDS
COD
OIL I OREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DISS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
•EMZENE
CHLOROBENIENE
I.I-DICIILOROETHANE
II2-TRAH8-DICHLOROETHYLENE
ETHYL BENZENE
HETHTLENE CHLORIDE
TOLUENE
PHENOL
li3-DICHLOROBEMZEHE
1.2-D1PHENYLHYDRAZINE
NAPHTHALENE
•IS<2-ETHrLHEXTL> PHTHALATE
DIETHVL PHTHALATE
ANTHRACENE
FLUORENE
PlfENANTHRENE
Ii2l3*4-DIBENZANTHRACENE
CADMIUM
CHROMIUM
COPPER
CTANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
•ARIUH
•ORON
CALCIUM
COBALT
IRON
HAONCB1UH
MANGANESE
POLLUIANIS NOI LIBIED MERE NOT DETECTED AT ANY SAMPLE POINT
L-LE39 TKANI N-D
-------
MASS RETURNED TO PLANT JM POUNUB fER DAT
FOK 8AWLE PATE EMItlMO BI02I2 AT OBOO HOURS
OlOESTEft VACUUH FILTER TOTAL MAB8
FRACTION PARAHCIER 8UPERMATANT FILTRATE RETURNED
NON-COMV. HETAL8 SOBIOH 104 M.O UB
WANAfilUH L O.I L O.I L O.I
YTTRIUM L O.I L O.I .1
POILUTAN1S HOI LISTEli UEKE NUI HETtCIED AT ANT SAMPLE POINT
L'LESS I HAM I H [I'HOI titTtCTEb.
-------
MASS BALANCE IM POUNDS PER DAY
FRACTION
CONVENTIONAL6
NON-CONVENTIONALS
NJ
VOLATILEB
FOR SAMPLE DATE ENDING 810211 AT 0800 HOURS
PARAMETER
HOP
TOTAL SUSP. 8ULID9
COP
OIL I GREASE
TOTAL PHENOLS
tOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. BOLIPB
TOTAL VOL. SUB. SOLIDS
AMMONIA NITROGEN
TOC
PENZENE
CHtOROkEHZENE
I,I,I-TRICHLOROETHANE
CHLOROFORM
£THYLPEN2CNE
METHTLENE CHLORIDE
TEtRACHLOROETHYLENE
TOLUENE
TRICIILOOOETHYLCNE
2>4t4-TRICHLOROPHENOL
2-CHLOROPHENOL
2t4-DICHLOROPHENDL
PENTACHLOROPHEHOL
PHENOL
||2>4-!RICHIOROBENZENE
I>3-DICHLOROBENZENE
FLUORANTHENE
NAPIITHAtEHE
PIBI2-ETHYLHEXYL) PHIHALATE
I»2-»ENZAHTKRACENE
BENZO
-------
NABS BALANCE IN FOUND! PER PAY
SAMPLE PATE t Nil I HO 010313 AT 0000 HOUR!
FKACTION
HE TALI
NOH-CONV. KETALB
PARAMETER
MERCURY
NICKEL
BUYER
ZINC
ALUHINUH
BARIUM
BORON
CALCIUM
COBALT
IKON
NAONEIIUH
MAHOAMCBE
INFLUENT
TOTAL*
OUT
N-D
31. r
2.t
199
L O.I
30.9
231
33.4
27.1
IBB74
2.3
133*
2*34
12*
EFFLUENT
N-0
.4
44.0
149
*.2
23.0
17212
l.t
PR IN ART
•LUMK
SECONDARY
BLUDOE
NJ
NJ
TITANIUM
VANADIUM
N-0
3.4
72. •
•0032
29.7
N-B
L O.I
1.9
.9
27,1
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
N-B
4)3
181
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
» TOTAL HASS GUI IS HOI ADJUBIED b» HASS CONTAINED IN RETURN FLOUB
POtLUTANTS NUT LI6FEU HIKE NOT DETECTED AT ANT SAMPLE POINT
L-LE6S THANI N-0'N01
-------
fKACTION
CONVENTIONAL8
MON-CONUENTIONALB
VOLATILES
N)
OJ
MASS BALANCE IN POUNliS FCft t'AY
FUR SAMPLE PATE ENDING 810214 AT 0800 HOURS
PARANETER
BOD
TOTAL 8U9P. SOLI 1*8
COti
OIL I GRCA8E
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE BOLItiS
VOLATILE DIS9. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
DENZENE
CMLORODENZEHE
Iild-TRICHLOROETHANE
CHLOROFORM
1,2-TRANS-PICHLOROETIITlENE
ETHYLBEHZENE
HETHYLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2-CHLOROPHENOL
2>4-DICHLOROPHENOL
2.4-DIHETHYLPHENOL
PHENOL
I>2(4-TRICMLOROBENZENE
FLUORANTHENE
4-CKLOKOPHENVl PHENYL ETHER
NAPHTHALENE
BIS(2-ETHYLHEXYL> PHTHALATE
DIETHYL PHTHALATE
1,2-PIHZANTHRACENE
lii12-BEMZDFLUDfiAHTH£HE
CHRYSENE
ANTHRACENE
FLUORENE
PHENANTIIRENE
PYKKNE
ANTIMONY
ARSENIC
HERYLLIUM
CADMIUM
CHROHtllH
COPPER
CYANIDE
* TOTAL MASS OUT 18 NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTEP HERE NOT PETECTED AT ANY SAMPLE POINT
I-IISS THAN) N-Ii*NDI liEUCIEIi.
ACID EXTRACT
UASE-NEUTMAL8
METALS
INFLUENT
10208*
84730
231808
27903
442
439331
339400
9BOOI
3380*
42193
3403
102064
2.7
N-0
2.7
20.4
.3
9.4
13.3
4.1
34. 4
2.7
.3
N-D
1.4
1.4
2.0
H-l>
M-D
4.4
H-P
HO
H-D
M-B
N-D
H-P
N-h
N-D
M-B
N-l<
N D
II D
N-fc
44.2
27.2
40.2
TOTAL*
OUT
122728
334311
348742
25426
23.8
623871
291241
237203
38382
198884
2813
101194
.7
I O.I
L O.I
9.3
H-P
.1
8.3
1.3
3.3
.a
M-D
.4
.4
2.1
3.4
4.3
.2
1.0
L 0.1
1.7
2.4
1.4
2.2
1.4
L 0.1
1.4
.2
1.4
4.4
1.4
3.9
393
82.3
IIB
EFFLUENT
13338
4344
23744
IBIf
18.2
270997
244431
34072
31923
4347
2423
17278
.4
H-P
N-0
9.1
N-D
N-D
8.3
1.2
4.3
.3
N-D
.4
.4
1.2
N-D
N-D
M-D
.4
N-D
N-D
N-D
M-B
N-D
N-D
N-D
N-D
H-I>
N-D
N-D
N-D
N-D
34.4
23.3
103
PRIMARY
SLUDGE
13827
48489
44314
4843
2.2
70388
1852
29122
389
28803
30.1
4748
L 0.1
L O.I
L O.I
.1
N-0
L O.I
N-D
L O.I
.7
L O.I
N-P
N-D
N-0
.9
1.2
.2
.2
.4
N-0
1.7
N-0
H-D
N-D
N-D
L 0.1
.2
.2
.2
1,9
.1
.3
39.4
12.2
1.0
SECONDARY
8LUDQE
93343
239434
298480
18944
3.4
284284
24738
172011
4477
143334
340
79148
L 0.1
N-D
N-P
.3
N-D
L O.I
N-D
N-D
.3
.3
N-D
N-D
N-D
N-D
2.2
4.1
N-D
N-D
L O.I
N-D
2.4
1.4
2.2
1.4
N-D
1.4
H-P
1.4
4.7
1.3
3.4
317
44.8
11.9
-------
MASS fcALAMCE IN POUNDS UK DAY
FOR SAMPLE DATE ENDINO 010914 Al 0800 HOURS
FhACT I OH
METALS
NUN-CONV. METALS
?
N>
PARAMETER
LEAD
MERCURY
NICKEL
BCLCHIUH
SILVER
ZIHC
ALUMINUM
•ARIUH
•Oft ON
CALCIUM
COIALT
IRON
HAONEBIUH
HANOANESE
SODIUM
TITANIUM
VANADIUM
INFLUENT
TOTAL*
OUT
N-D
.3
34.0
N-D
3.4
141
12t4
17,4
40, a
13433
3.7
1430
2722
114
47.2
L O.I
40.0
L O.I
f.3
277
M-P
2.4
CFFLUCHT
H-D
H-D
23.3
N-D
.3
42,4
I3t
7.4
41.9
13338
2.7
33%
2429
43.7
•3148
17.3
N-D
PRIMARY
•LUDOE
7.4
L O.I
4.9
L O.I
.»
41.7
HOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
•Luooe
3>. 4
N-D
30,2
N-D
• .3
173
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN '
I (OTAL MASS OUT IS NOT ADJUSTED >Y MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS THAN! H-D-NOT DETECTED.
-------
FRACTION
CONVENTIONAL9
MOM-CONVENTIONAL8
VOLATILE8
Ul
ACID EXTRACT
»ASE-NEUTRALS
METALS
NON-CONV, NETAL8
PARAMETER
DOD
TOTAL SUSP,
COD
OIL 1 OREA8E
NAS8 BALANCE IN POUNDS PER DAY
FOR SAMPLE tiATC ENt'INO 810213 AT 0800 HOURS
SOLIDS
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL KISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE MSB. SOLIDS
TOTAL VOL. 9US. SOLIDS
AMMONIA NITROOEN
TOC
DENZENE
lilfl-TRICHLOROETHAHE
1.112-TRICHlCROC THANE
CHLOROFORM
ETHYLBENZENE
METHYLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2>4-DICMLOROFMENOL
PHENOL
ti2f4-IRICHLOROI FMTHALATE
DIETHYL PHTHALATE
ACENAPHTHYLENE
ANTHRACENE
PMENANTHREHE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
tiORON
INFLUENT
90004
34144
212413
loaoi
414
444428
388824
107447
44804
42B43
4120
100804
3.2
1.8
N-D
19.8
H-D
SO. 4
7.4
7?. 2
1.4
.7
148
H-D
N-D
4.0
1.
1.
•
.
•
N-D
N-D
N-0
H-D
SO. 4
28. B
4.8
N-D
21.8
.7
82. a
943
24.3
39, 4
TOTAL*
OUT
34477
279943
374040
23280
33,7
429318
34444V
334358
191321
143037
3873
33341
.4
L O.I
.1
11.8
,7
13.2
1.7
7.3
1.4
.3
7.3
2,2
L 0,1
.2
3.4
H-D
H-»
N-D
N-D
1.3
7.3
1.1
2,4
306
47,8
24.0
33.2
31.4
8,3
207
-
-
-
EFFLUENT
19407
7114
43284
2244
23.9
311137
321434
188897
184349
4S28
121S
24382
.4
M-D
H-D
10.7
.4
IS. 2
1.1
4.9
1,1
,3
4,9
H-D
N-D
N-D
1.4
N-D
H-D
H-D
N-D
H-D
N-D
N-D
H-D
11.0
13.4
14.4
N-0
18.8
.3
38.8
171
8.4
38.8
PRIMARY
8LUDOC
4014
32443
24904
1240
2.6
34184
1804
189*2
473
16318
28.3
2849
L O.I
L O.I
H-D
.1
L 0.1
H-D
L O.I
.3
L 0.1
H-D
.8
N-D
L O.I
.2
M-D
N-P
H-D
H-D
H-D
L O.I
.7
L O.I
.2
11.3
7.4
.4
4.4
3.3
,4
28,3
HOT RUM
NOT RUN
NOT RUN
SECONDARY
SLUDOE
31034
240384
323870
19794
3,0
241973
21411
128449
4477
121991
412
23910
H-D
H-D
.1
1.0
H-D
N-D
.3
,7
.2
H-D
H-D
2.2
H-D
H-D
H-D
N-D
H-0
N-D
N-D
1.4
4.8
1,0
2.2
284
44.8
10.8
30.4
29.1
7.4
140
NOT RUN
NOT RUN
NOT RUN
* TOTAL MASS OUT IS NOT ADJUSTED DY MASS CONTAINED IN RETURN FLOWS
FtllLUTANrS HOT LISUP MERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS TMAMI N-P'HOT DETECTED.
-------
HA8B BALANCE IN POUNU6 ft* DAY
FOR 8ANPLE I
-------
MASS BALANCE IN POUNDS PER DAY
FRACTION
CONVENT10NALS
NDH-CONVEHTIOHALS
VOLATILES
NJ
-J
ACID EXTRACT
VASE-NEUTRALS
METALS
PARAMETER
•OD
TOTAL SUSP
COD
OIL t GREASE
FOR SAMPLE DATE EHPIHO 81021* AT 0800 HOURS
SOLIDS
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL PISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
BENZENE
Irl.l-TRICHLOROETHANE
CHLOROFORM
I.2-TRANB-DICMLOROETHYLENE
ETHTLtENZENE
HETMVLEHE CHLORIDE
TETRACHLOROE TMYLENE
TOLUENE
TRICHL OROE T HTL EHE
214-DICHL OROPHE NOL
PENTACHLOROPHEHOL
PHENOL
ACCNAPHTHENE
lf2>4-TRICHLOROBEHZEHE
li3-DICHLOROBEMZENE
FLUORANTHENE
PI8(2-CHLOROETHYOXY> METHANE
NAPHTHALENE
>IS<2-ETHYLKEXYL) PHTHALATE
ACEHAPHTHYLENE
FLUOREHE
PHENANTHKENE
ANTIMONY
ARSENIC
DERYLLIUH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAP
MERCURY
NICKEL
SILVER
ZINC
INFLUENT
41037
41017
9742B
4298
219
224370
182334
34737
I037S
2*3*3
3132
40117
3.4
1.4
9.7
.*
2.«
7.2
3.4
77.4
2.3
.9
N-0
40.2
.3
1.7
.4
N-D
3.4
4.4
2.4
.*
N-D
N-D
N-D
N-D
N-D
N-D
B.3
16.?
32.4
25.2
N-D
H-D
.«
43.0
TOTAL*
OUT
42984
213149
3172*5
24018
12.2
414783
203811
17*774
329*0
14361*
2*33
29400
.8
L 0.1
8,3
N-D
L 0.1
203
.1
3.0
L 0.1
N-D
L O.I
2.7
N-D
2.1
N-D
.2
H-D
.3
N-D
N-D
L 0.1
.1
,8
3.3
.8
2.3
291
80.9
IS. 9
29.*
L O.I
71.9
7.1
214
EFFLUENT
4313
4258
323*3
N-D
• .3
IB7III
1B2833
29807
27092
2799
2004
12023
.8
H-D
7.9
N-D
N-D
209
N-D
3.8
N-D
N-D
N-D
2.3
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
7.0
33.1
8.3
N-D
N-D
42.*
.3
30.1
PRIMARY
BLUPQE
3323
199*7
18409
7845
1.4
20938
98*
12023
310
11313
3*. 8
1983
L O.I
L 0.1
.3
N-D
L 0.1
N-D
L 0.1
.7
L 0.1
N-D
L 0.1
.4
N-D
.2
N-D
.2
N-D
.3
N-D
N-D
L 0.1
.1
.1
1.2
L O.I
.1
14.2
4.2
.*
4.6
L 0.1
3.8
.3
24.1
SECONDARY
SLUDOE
30946
188924
2«*293
IB173
2.3
20871*
19972
13494*
3396
129946
412
13474
N-0
H-D
.7
N-D
N-D
N-D
.1
.3
N-D
N-D
N-D
N-D
N-D
1.9
H-D
N-D
N-D
N-D
H-D
N-D
N-D
H-D
.7
4.3
.8
2.2
230
39.*
4.8
24.6
H-D
23.9
4.3
140
« TOTAL MASS OUT IS NOT ADJUSTED PY MASS CONTAINEIi IN RETURN FLOWS
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POIMT
L'lESB THAN* N-P-NOT DETECTED.
-------
NAS9 ftALANCE IN POUNP8 UK PAY
FOR SAMPLE DATE ENUINO BI03U AT 0800 HOURS
FRACTION
WON-CONV. METALS
PARAMETER
ALUMINUM
•ARIUH
tOROH
CALCIUM
COIlALT
I ROM
MAOHE8IUH
MANGANESE
SODIUM
TITANIUM
INFLUENT
TOTAL*
OUT
EFFLUENT
PRIMARY
8LUDOC
I02»
23.9
21.2
13794
1.4
729
3292
BB.S
42123
N-D
tS.2
4.3
10.3
12274
1.9
>9.2
2294
42.4
19.1
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
SECONDARY
ILUDOC
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT HUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUH
NJ
00
I TOTAL MASS OUT IS NOT ADJUSTED »Y MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
I-IESS THAN) N-ti«NOt DETECTED.
-------
MASS BALANCE IN FOUNDS PER PAY
FKACTtON
COMVENTIONALS
NON-CONVENTIONAL6
o
r\j
VULATILEB
FOR SAMPLE PATE ENPINO 810317 *f OBOO HOURS
PARAMETER
POD
TOTAL SUSP. SOLIDS
COD
OIL I CREASE
TOTAL PHENOLS
TOTAL BOLIDB
TOTAL DIBS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOTAL VOL. SUB. 80LIDB
AMMONIA NITROOEH
TUC
BENZEHE
CHLOROBEHIENE
l.l.l-TRICHLOROETHAME
Itl-DICHLOROETHANC
I»I»2>2-TETRACMLOROETHANE
CHLOROFORM
CTHYLBEHZENE
HETHYLENE CHLORIDE
TETRACHLOROETHYLEHE
TOLUENE
IRICHLOROETHYLENE
2 > 4- DICHLOROPIIENOL
PHENOL
ACENAPHTHEHE
l>2i4-TRICHLORODEHZEHE
HEXACHLOROETHANE
I r3-DICHLORO»ENZENE
l«4-DICHLOftO»EHZEHE
2.4-DINITROTOLUENE
FLUORANTHENE
»IS(2-CHLOKOETHYOXY> METHANE
NAPHTHALENE
BIS(2-ETHVLHEXYLI PHTHALATE
ACEHAPHTHYLENE
ANTHRACENE
FLUORENE
PHENANTHRENE
PYREHE
ALPHA-DHC
ANTIMONY
ARSENIC
DEKYLLIUM
CADMIUM
* TOIAL MASS OUT IS NOT ADJUSTED BY HASS CONTAINED IN RETURN FLOWS
POllUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS THANI N-D-MOT DETECTED.
ACID EXTRACT
•ABE-NEUTRALS
PESTICIDES
METALS
INFLUENT
104729
•200B
224410
14831
337
901183
407478
13*882
•3032
94B91
374«
*7244
7.9
H-D
2.4
N-D
N-D
44.*
12.7
14.2
187
3.7
.7
*7.2
.4
3.0
N-P
.7
2.2
N-D
N-D
7.9
N-D
9*. 8
I.I
.4
.7
.4
N-D
N-D
N-D
H-0
H-D
1.*
TOTAL*
OUT
128440
2*344*
348249
2VB4*
23.3
984370
2*0742
140743
48823
1120*4
3340
77473
1.4
L 0.1
N-D
L 0.1
L 0.1
14.3
1.3
7.4
I.I
1*.4
.5
N-D
3.4
L 0>l
2.2
L O.I
N-D
N-D
L 0.1
1.*
H-D
,4
N-D
N-D
.3
.1
.3
.2
L O.I
1.3
10. 3
I.I
2.9
EFFLUENT
*7*4
*7*4
37194
1013
17. f
273*41
244149
4742?
41889
9742
2702
1384*
1.4
H-D
N-D
H-D
H-D
15.2
1.0
7.4
.7
18,4
N-D
N-D
2.7
N-D
N-P
N-P
N-P
N-P
N-D
1.7
N-D
N-D
N-D
H-D
H-D
H-D
H-D
N-D
H-D
H-D
H-D
N-Ii
H-B
PRIMARY
SLUDOE
22198
42100
93813
B447
1.8
43841
1729
1*191
904
18802
30.1
4447
L O.I
L 0.1
N-D
L Otl
L O.I
.1
.3
H-D
N-D
1.0
.4
H-D
.7
L O.t
.8
L O.I
H-P
N-P
L O.I
.2
N-P
.4
N-D
N-D
.3
.1
.3
.2
L 0.1
.1
3.4
.2
.4
SECONDARY
SLUDOE
*44B4
241973
2972*7
2034*
3.4
244988
24872
*3*89
4432
•7992
408
97177
N-P
N-P
N-D
N-D
N-D
1.0
H-P
N-D
.4
N-D
L 0.1
N-D
N-D
N-D
1.4
N-D
N-D
N-D
N-D
H-P
N-D
N-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
1.2
14.7
.*
2. 1
-------
MASS bALANCE IN POUNB8 UK PAY
FOR SAflFlE If Ml ENDIMO •1021? AT OBOO MOUNS
FKACMON
METALS
PARAMETER
NDM-CONV. Mi I AtS
UJ
O
CMKONIUH
COPPER
CYANIDC
LEAD
MCKCUKY
NICKEL
SELENIUM
SILVER
ZINC
ALUMINUM
BAKIUH
BORON
CALCIUM
COBAL T
IKON
NAONEBIUH
NANOANEBC
SODIUM
VANADIUM
INFLUENT
92.4
IS. 9
123
14.4
.4
21,7
4.9
1.7
TOT*
OU1
290
49,
l».
44.
L
14.
L
».
>L»
r
.1
.1
EFFLUENT
B.4
4.B
II. •
N-B
H-D
H-D
N-D
.1
PHI MART
BLUDOE
2B.9
19. B
4.1
11. 1
L O.I
7.4
L O.I
1.4
SECONDARY
BLUDOE
214
42. f
1.1
12. f
N-D
20.4
N-D
7.1
211
21»2
4B.4
94.1
IB70I
4.»
1111
3344
120
244
17.2
199
».B
40.9
19074
1.7
142
2702
II.I
•01*2
H-D
9B.4
NOT KUN
NOT RUN
HOT HUN
NOT KUN
NOT HUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
190
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
« lOJflL MASS OUF IS MOT AIIJUB1CD BY MASS CONTAINED IN REIUKN FLOMB
POLLUTANTS NOT LISTED HEftE NOT DETECTED AT ANY SAMPLE POINT
L-IEOS THAN! N-fi-NOf DETECTED.
-------
MASS BALANCE IN POUNDS PER DAY
FOR SAMPLE IIATE ENDING 010210 AT OBOO HOURS
FRACTION
CONVENTIOMALB
NON-CONVEHTIONALB
VOLAT1I.ES
U)
PARAMETER
IOD
TOTAL SUSP. SOL 108
COO
OIL I OREABE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROGEN
TOC
tENZENE
1,1.1-TRICHLOROETHANE
1,1-DICHLOROETHANE
CHLOROFORM
l.l-OICMLOROETHYLENE
ETHYLDENZENE
HETHTLENE CHLORIDE
TETRACHLOROETHYLEHE
TOLUENE
TRICHLOROETHYLENE
2«4-DICHLOROPHENOL
2.4-DIMETHYLPHENOL
4-NITROPHENOL
PHENOL
ACENAPHTHENE
li2(4-TRICHLOROBEMZENE
lr3-DICHLOROBENZENE
FLUORANTHENE
BIS<2-CHLOROETHYGXV> METHANE
NAPHTHALENE
BIB(2-ETHYLHEXYL> PHTHALATE
•UTYL BENZYL PHTHALATC
DI-N-BUTVL PHTHALATE
FLUORENE
PHENANTHRENE
PYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LCAO
« IOTAL MASS OUT IS NOI ADJUSTED «Y MASS CONTAINED IN RETURN FLOUS
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
L--LEBS T1IANI N-D-NOI DETECTED.
ACID EXTRACT
BASE-NEUTRALS
METALS
INFLUENT
72333
93243
134S02
9*18
198
284070
330807
87128
998*3
31239
1*73
9*181
8,*
78.*
N-D
19. 1
4.*
4.*
IB. I
7. A
128
3.3
4*4
N-D
N-D
J*,9
N-D
4.*
1.0
N-D
9.3
3.4
1.3
N-D
N-P
N-D
N-D
N-D
N-D
N-D
N-D
1.4
18.4
23.0
13.3
28.4
TOTAL*
OUT
209029
30741*
3821*7
31942
27.1
979*18
248931
158134
34991
123974
1494
1371*7
1.4
21.2
L 0.1
18.8
.3
3.1
11.7
1.*
*.o
.8
,y
.3
14.9
1.2
L 0,1
4.0
1.3
.2
N-D
1,*
.4
34.2
.4
.1
.3
.2
,v
10.4
1.2
3.2
217
41.2
19.0
90.3
EFFLUENT
847*
7402
39084
N-D
24.4
29241*
249017
347*4
2*823
4*71
1442
14*12
1.2
13.8
N-D
18.1
.3
2.*
11.7
1.8
8.2
.4
.*
.3
N-D
1.2
N-D
.4
1.3
N-D
N-D
H-D
.4
N-D
.4
N-D
N-D
N-D
N-0
N-D
N-D
N-D
8.2
3.8
12.*
N-D
PRIMARY
SLUDGE
I8**2
44931
42733
44*9
1.1
48272
1773
28429
380
28014
11.1
4331
H-D
4.0
t 0.1
.1
N-D
H-D
H-D
L O.I
.8
L O.I
N-0
H-D
H-D
N-D
L O.I
1.1
H-D
.2
N-D
.9
N-D
N-D
N-D
.1
.3
.2
L O.I
1.3
L O.I
.3
10.1
10.3
1.0
10.4
SECONDARY
SLUDOE
177394
293284
304378
17047
1.4
279027
21741
*4»I7
4348
*098*
181
119*54
.4
1,4
N-0
.4
N-D
.2
N-D
N-D
H-D
.1
N-D
N-D
14.9
N-D
N-D
4.3
N-D
H-D
H-D
1,4
H-D
34.2
H-D
N-D
N-D
N-D
.*
*. 1
1.2
2.9
1**
47.1
I.I
37.9
-------
MASS HAI.ANCE IN POUNDS PER VAT
FUR SAMPLE DATE ENDINO 810210 AT 0«00 HOURS
FKACIION
METALS
H(JM CUMV. METAIS
PARAMETER
MERCURY
NICKEL
SILVER
2IHC
ALUMINUM
IARIUM
IORON
CALCIUM
COtALT
IRON
HAONESIUM
HAHOANCSE
SODIUM
INFLUENT
TOTAL*
OUT
N-B
1.1
*3.1
10*2
27. »
2*.0
1380*
«.r
1001
I 0.
10.0
9.7
23*
72.1
92277
EFFLUENT
N-D
N-D
.1
18.0
I2f
7,4
2t,2,
IIA»9
2.1
123
2047
38.9
74*90
PRIMARY
SLUDOE
L O.I
4.3
I.I
It. 4
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
HOT RUN
HOT RUN
NOT RUN
SECONDARY
ILUDOE
N-D
11.7
8.3
178
HOT RUN
HOT RUN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUM
U)
Is)
I IOIAI MASS OUT IS NOT ADJUSTED M MASS CONTAINED IN RETURN FLOUS
POLLUTANTS NOT LISTED UEKE NOT DETECTED AT ANY SAMPLE POINT
L»LtSS THANI N-D-NOI DETECTED.
-------
FRACTION
CONVENT10HALB
NOM-CONVENTIONALB
VOLATILE8
U)
U)
rtABB RETURNED TO FLANT IN POUNDS PER HAY
FOR SAMPLE DATE ENDINO 010218 AT 0800 HOURS
PARAMETER
•UP
TOTAL SUSP. SOLIDS
COD
OIL I OREASE
TOTAL PHENOL*
TOTAL SOLIDS
TOTAL DIBS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI8B. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
•EMZEME
CHLOROBENZENE
1,1-DICHLOROETHAHE
1>2-TRANB-DICHLOROETHTLENE
ETHYLPENZEHE
HETHYLENE CHLORIDE
TOLUENE
PARACHLOftOHETA CRESOL
2-CHLOftOPHENOL
2>4-DICHLOROPHENOL
PHENOL
I.J-DICHLOROBENZENE
Itl-ttlCHLOROBEMZEHE
1>2-DIPHENYLHYDRAZINE
NAPHTHALENE
NITROBENZENE
DI8<2-ETHYLHEXYL> PHTHALATE
DI-N-KUTYL PHTHALATE
METHYL PHTHALATE
ANTHRACENE
PHENANTHRENE
CADNIUH
CHROMIUM
COPPER
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
BORON
CALCIUH
COIALT
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L-LE93 THANI N-D-NOT DETECTED.
ACID EXTRACT
BASE-NEUTRALS
HETALS
NON-CONV. HETALS
UIOESTER VACUUM FILTER TOTAL DABS
SUPERNATANT FILTRATE RETURNED
37.9
81.0
12?
S.2
.1
170
290
00.0
34.0
44.0
11.0
47.9
L 0
L 0
t 0
I 0
L 0
L 0
L 0
L 0.
H-0
H-D
L 0.
L 0,
1
1
t
L Oil
N-D
H-D
L 0.
L 0.
L 0.
H-D
L 0.
L 0.
L 0.
.1
L 0.
L 0.
L 0.
L 0.
L 0.
.2
4.4
.1
L 0.
53.2
L 0.
1
1
1
1
1
1
1
1
1
t
1
1
1
10. S
111
9S.O
2.0
L 0.
447
US
34.0
32.9
23.9
19.0
31.2
U 0.
N-D
H-D
H-D
H-D
L 0.
L 0.
N-D
L 0.
L 0.
L 0.
N-D
N-D
L 0.
L 0,
N-D
L 0.
H-D
L 0.
N-D
N-D
N-D
L 0.
L 0.
L 0.
L 0.
H-0
L 0.
L 0.
1.1
L 0.
L 0.
70.9
L 0.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
38.0
1*2
182
7.2
.2
817
429
134
88.9
47.9
24.0
7B
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
L
9
L
.7
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
Ot
.1
0.
0.
0."
0.
0.
.3
.3
.1
0.1
124
1
L
0.1
-------
MASS RETURNED TO PLANT IN POUNDS PER PAT
FOR SAMPLE PAIE ENDING 810218 AI OSOO HOURS
FRACIION
HON-CONV. METALS
PARAMETER
IRON
MAOMMIUM
MAMOANESE
HOLYWENUH
SODIUM
TITANIUM
VANADIUM
VITRIUN
DIGESTER
SUPERNATANT
3.1
7.0
.9
L O.I
44.2
L 0.1
L O.I
I 0.1
VACUUM FILTER
FILTRATE
1.3
f .2
.4
N-V
tJ.O
M-e
L O.I
L 0,1
TOTAL MAiS
RETURNED
4.4
U.2
1.1
I O.I
107
L O.I
L O.I
L 0.1
POLLUTANTS NUT LISTED UCftC NOT DETECTED AT ANT SAMPLE POINT
L-LESS TIIANI N-D-NOT DETECTED.
-------
MASS BALANCE IN POUNDS UK OAT
FRACTION
CONVENTIONALB
NON-CONVEHTIONALB
O
I
CO
en
VOLATILEB
FOR SAMPLE DATE ENDING 81021* AT 0800 HOURS
PARAMETER
ion
TOTAL SUSP. SOLIDS
COD
OIL I CREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DtSB. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI8B. BOL1DB
TOTAL VOL. BUS. SOLIDS
AHHONIA HITROOEN
TOC
BENZENE
1,1,1-mCHLOROETHANE
l.l-DICHLOROETHAKC
l*lr2t2-TETRACHLOROETHANE
CHLOROFORM
ETHTLIENZENC
HETHYLEHE CHLORIDE
TETRACHLOROETHVLENE
TOLUENE
TRICHLOROETHYLENE
2t4t4-TRICHLOROPHENOL
2.4-D1CHLOROPHENOL
PHENOL
ACENAPHTHENE
I>2>4-TRICHLORO«EHZENE
I.3-DJCHLOROBENZEHE
1.4-D1CHLOROBENZENE
FLUORAHTHENC
NAPHTHALENE
BIBI2-ETHVLHEXYL) PHTHALATE
DI-N-DUTYL PHTHALATE
DIETHYL PHTHALATE
PHEHANTHkEHE
PYRENE
ANTINOMY
ARSENIC
BERYL!IUN
CADMIUM
CIIROHIUN
COPPER
CYANIDt
LEAD
NERCURY
NICKEL
* TOIAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOUB
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
I-LESS THAN) N-D'NOT DETECTED.
ACID EXTRACT
•ASE-NEUTRAIB
METALS
INFLUENT
44034
34130
110040
2201
134
2*4282
242132
84727
39470
31237
2201
37231
11.4
4.4
«-D
1.3
IB.?
7.V
2*. 3
ITS
134
34.3
N-D
3.3
44.0
14.3
2.2
•
1.
N-D
2,
1.
• *
•
N-D
N-D
N-D
N-D
N-D
N-D
23.3
IV. 8
7.3
37.0
H-D
88. 0
TOTAL*
OUT
II8414
2313*7
303034
37347
3.3
488403
237lfO
IBVBIf
20804
14*022
387
34240
,8
1.4
L O.I
N-D
12.3
L 0.1
18.4
10.7
1.3
L O.I
2.4
2.4
.8
N-D
3.7
N-D
N-D
L 0.1
L O.I
B*,0
N-D
N-D
L O.I
L O.I
1.2
11.2
1.4
2.4
230
90.2
14.*
44.3
L O.I
8V. 1
EFFLUENT
S441
11321
347*3
1417
3.3
231281
2I**40
24484
181*3
84*1
404
13343
.8
1.4
H-D
H-D
12.3
N-D
IB. 4
7.7
1.2
N-D
2.4
2.4
,8
N-D
M-D
N-D
H-D
N-D
N-D
BT.O
N-D
H-D
N-0
N-D
N-D
N-D
N-D
H-D
30.3
N-D
4.*
N-D
N-D
3B.4
PRIMARY
BLUDOE
4**B
122*7
*I43
312
.2
12420
317
4*34
*l.4
4872
2.*
12*1
L 0.1
L O.I
L 0.1
N-D
t 0.1
L O.I
N-D
.1
.]
L 0.1
N-D
N-D
N-D
N-D
L O.I
H-D
N-D
L 0.1
L O.I
N-D
N-D
N-D
L O.I
L 0.1
L O.I
,4
.1
L O.I
4.2
3.4
.4
3,1
L 0.1
3.V
SECONDARY
BLUDOE
107*37
22778*
23*0*4
33418
N-D
244702
14*13
134177
231*
13343*
180
3*384
N-
N-
N-
N-
N-
N-
N-
2
N-
H-
H-
N-
H-
H-
3
N-
N-
N-
N-
H-
H-
»
4
N-D
N-D
H-D
1.2
10.8
1.3
2.3
214
44.8
7.4
43.2
N-D
44.8
-------
MASS BALANCE IN POUNDS PER PAY
FOR SAMPLE DATE ENDING BIQ311 AT 0000 HOUKB
FRACTION
MtTALS
NUN-CONV. METALS
PARAMETER
SILVER
ZINC
ALUMINUM
DARIUM
BORON
CALCIUM
COiALT
IKON
MAONE8IUN
MANGANESE
SODIUM
VANADIUM
riTKIUM
INFLUENT
TQIALI
OUf
EFFLUENT
PRIMARY
iLUPOE
•ECONDARr
ILUbOE
I.a
110
19*1
31 .7
24.7
IB490
7.3
IMS
2441
»*.?
3170V
2.2
4.4
a.t
237
.4
11.4
22«
11.3
24.7
U37B
3.7
23f
242*
72.8
333»4
N-0
N-D
.2
12.?
NOT RUN
NOT NUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
8.1
NOT RUN
NOT RUN
HOT RUM
NOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUH
HOT RUH
HOT RUH
HOT RUN
( IOIAL MASS OUT IS NOT ADJUSTED *T MASS CONTAINED IN RETURN FLOUS
fOLLUTAHIB NOT LISTED WERE NOT DETECTED AT AMY SAMPLE P01HT
L-IE8S THANI N~D*N01 DETECTED.
-------
MASS BALANCE IN POUNDS UK DAY
FOR SAMPLE PATE ENPINO 110220 AT OBOO HOURS
FRACTION
CONVENTIONAL*
NON-CONVENTIONALS
?
OJ
VOLATILE8
ACID EXTRACT
BASE-NEUTRAL*
HETAIB
PARAMETER
too
TOTAL SUSP. SOLIDS
COP
OIL I OREA8E
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBB. SOLIDS
TOTAL VOL. SUB. SOLIDS
AMMONIA N1TROOEN
TOC
DENZENE
1 • I > 1 - TRICHLOMOE THAW
CHLOROFORM
ETHYLIENZENt
HETHTLCNE CHLORIDE
TETRACHLOROCTHVLCNE
TOLUENE
TRICHLOROETHYLENC
2.4-DICIILOROPMENOL
3.4-DIHETHTLPHENOL
PHENOL
l«2f4-TRICHLOROIENZCME
t«2-DICHLOROIENZENE
I>3-DICHLOROSENZENE
l>4-DICIILOftOBENZENE
NAPHTHALENE
»I8(2-CTHYLHEXVL> PHTHALATE
PI-N-IUTTL PHTHALATC
DI-N-OCIYL PHTHALATC
DIETHYL PHTHALATE
PHEHANTHRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANltiE
LEAP
HCRCURY
NICKEL
SILVER
ZINC
INFLUENT
12124*
61340
208974
2*10
243
403307
31*147
123304
73731
4*47*
2429
B0014
4.4
2.»
28.4
2S.4
43.7
93.3
34.4
I.S
3.4
N-B
44.1
9.3
N-P
1.0
11.2
.9
1.0
1.0
N-D
N-P
N-D
N-D
N-P
N-D
N-D
2*. 4
23.3
S3.S
N-D
N-D
98.2
l.»
107
TOTAL*
OUT EFFLUENT
838*4 »B7B
2833*7 43103
3130B2 74128
14494 1347
7,2 4.7
974424 3I31B?
2*3234 3720B4
184874 44490
41327 34817
143944 2*433
1474 1347
71494 24041
1.3 1.3
N-D H-D
14.2 19.3
1.
IS.
10.
1.
L
•
1.
1.
4.
13.
N-D
L
•
2.
A f
17.
1.
L
1.
II.
1.8
18.4
*.4
1.3
.1 N-D
.*
1.3
I.S
3.1
11.2
N-D
.1 N-D
N-D
2.7
4.9
17.9
1.8
.1 N-D
N-D
N-D
1.9 M-P
2,4 N-D
213 2*. 4
244 7.4
14.7 11.2
30.3 N-D
L O.I N-D
7V. 1 24.0
*.4 .»
240 47.3
PR 1 NARY
SLUDOE
2047
140*4
1*242
1108
.3
14739
434
*388
1*2
*2I3
9.2
9831
N-D
N-B
L O.I
L O.I
N-D
N-D
L O.I
L O.I
N-D
N-D
N-D
.2
.3
H-D
L O.t
.1
N-D
N-0
H-D
N-D
L O.I
L O.I
1.0
L 0,1
.2
4. a
4.1
.3
2.4
L O.I
9 19
,2
13.2
SECONDARY
SLUDOE
71*71
2241*0
21*912
121**
N-D
244702
20912
10*034
4318
104718
324
3*984
N-D
N-D
.*
N-D
N-D
I.I
H-D
N-D
N-D
N-D
N-D
3.9
2.2
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
.*
10.8
1.9
2.2
180
232
3.2
27.7
N-D
43.2
8.3
138
« TOTAL NABS OUT IS NOT ADJUSTED *Y NASB CONTAINED IN RETURN FLOUS
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
L-1E8S THAN) N-P->NOI DETECTED.
-------
NABS BAIANCE IN POUNDS PER PAT
FOR SAMPLE RATE ENMNO B10220 AT OBOO HOURS
FR ACTION
NON-CONV. METALS
PARAMETER
ALUMINUM
BARIUM
•ORON
CALCIUM
COIl ALT
IRON
HAONE9IUN
HANOANEBE
80PIUM
VANADIUM
INFLUENT
TOTAL*
OUT
EFFLUENT
2289
17,1
43.1
2089?
7.8
1444
1199
121
4»B4B
2.4
842
24,2
44. t
20491
4.)
43B
24*4
M.I
4734B
H-P
HUM ART
iLUtlOE
SECONDARY
BLUPOE
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
HOT RUN
HOT RUN
O
I
U>
00
$ TOTAL MASS OUT 18 NOT ADJUSTED BT MASS CONTA1NEP IN RETURN FLOUB
POLLUTANTS NOT LI8TEP MERE NOT PETECTED AT ANY SAMPLE POINT
L-LE86 THAN1 N-D-NOT PETECTED.
-------
FRACTION
CONVENTIONAL8
MON-CONVENIIONAL8
VOLATILEB
LO
v£>
MASS BALANCE IN POUNDS UK DAY
FOR SAMPLE PATE EMD1H0 810221 AT 0800 HOURS
PARAMETER
DOD
TOTAL SUSP. SOLIDS
COD
OIL I OREA6E
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHHONIA NITROOEN
TOC
DENZENE
1r1rI-THICHLOROE THANE
Irl-DICHLOROETHANE
Ir1t2-TRICHLOROETHANE
CHLOROFORM
l>2-TRANS-DICHLOROETHrLENE
ETHYLDENZEHE
NETKYLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TR1CHLOKOETHYLENE
VINYL CHLORIDE
2>4-DICHLOROPHEHOL
2i4-DIHETHYLPHENOL
PHENOL
tf2r4-TRICHLORO*ENZEHE
li3-DICHLOROBENZENE
NAPHTHALENE
DI8(2-ETHriMEXYO PHTHALATE
DI-N-DUTYL PHTHALATE
DIETHYL PHTHALATE
ANTHRACENE
PHENANTHRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADHIUN
CHROHIUN
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
* TOTAL MASS OUT IS NOT ADJUSTED DY NABS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY 8ANPLE POINT
I "I ESS THAN I N-D-.NOT PETECIEB.
ACID EXTRACT
DASE-NEUTRALB
HETALB
INFLUENT
77*34
«023t
129390
317*
222
307208
244930
91312
33233
38078
2937
37301
4.4
2.2
N-D
N-D
IB.S
.4
4.1
44.4
14. «
2f.2
1.8
N-D
1.9
N-D
28.9
14. B
1.9
8.9
1.8
3.9
3.*
.4
.4
N-D
N-D
N-D
N-D
44.4
23.3
74.3
N-8
,1
24.8
1.3
TOTAL*
OUT
44*81
243233
2?B17?
12412
10.8
488770
245314
1949*7
34304
138347
2082
327*1
1.0
N-D
L O.I
L 0.1
10.4
L 0.1
L 0.1
20.0
2.8
I.I
L O.I
L O.I
.3
.7
9.2
9,7
1.0
L O.I
.3
1.3
2.0
N-D
N-D
1.3
8.3
1.2
2.4
197
44. *
40.8
38.?
L O.I
33.1
9.2
EFFLUENT
7343
9348
32383
N-D
7.7
233042
223*94
3939*
32031
7343
U49
13*89
1.0
N-D
N-D
N-D
9.7
N-D
N-D
20.0
2.3
1.0
N-0
N-D
.3
.7
9.0
9.3
1.0
N-D
,3
1,1
2.0
N-D
N-D
N-D
N-D
N-D
N-D
7.7
N-D
34.4
N-D
N-D
N-D
.3
PRIMARY
SLUDOE
4*49
I7V93
17493
1308
,8
18742
790
9829
217
9379
17. S
3248
L O.I
N-0
L
I
L
L
L
I
L
L
L
L
N-D
N-D
.2
.1
N-0
L O.I
N-0
N-D
N-D
N-D
H-P
L O.I
.9
L O.I
.1
4.9
3.4
.2
2.2
L 0.1
8.3
.3
SECONDARY
8LUDOE
32971
2IS9I4
248301
10904
2.3
23498*
19072
149742
4318
141423
394
3382*
H-D
N-D
N-D
N-D
,7
N-D
N-D
N-D
.3
N-D
N-D
H-D
N-D
N-D
N-D
4.3
N-D
N-P
W-D
N-D
N-D
N-D
N-D
1.9
7.4
1.2
2,9
184
43,
*.
3*.
N-D
44.
8.
-------
HAS* DALANCE IN fDUMDS PER HAV
FOR (AMPLE OAIE ENDING 110221 AT 0100 HOURS
FRACTION
METALS
NON-CONV, METALB
PARAMETER
ZINC
ALUMINUM
MR I UN
DORON
CALCIUM
CODALT
IRON
MAGNESIUM
HANOANESE
SODIUM
TTTRIUH
INFLUENT
TOTAL*
OUT
EFFLUENT
PRIMARY
SLUDGE
SECONDARY
BLUDOE
f2.4
ISU
17.0
46.1
U41A
7.ft
lisa
2211
»».B
S»SI»
7.4
204
40.1
110
II.0
12.7
13J3S
3.1
140
2001
«*••
3S427
H-D
11.1
NOT RUN
NOT RUN
NOT RUN
HOT RUM
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
191
NOT RUN
NOT RUM
NOT RUN
HOT HUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
* TOTAL MASS OUT IS NOT ADJUSTED *T MASS CONTAINED IN REIURN FLOUS
POLIUIAMTS NOT LISTED HERE NOT OE1ECTED AT ANT SAMPLE POINT
L-LESS THANI N-D-NOT DETECTED.
-------
MASS BALANCE IN POUNDS Ft* DAY
FRACTION
CONVENT IONALB
NON-CONVENTIDMALS
VOLATILES
ACID EXTRACT
BASE-NEUTRALS
NETALB
PARAMETER
POP
TOTAL SUSP
COD
OIL I OREASE
FOR SAMPLE DATE END1NO 010222 AT 0800 HOURS
SOLIDS
TOTAL PHENOLS
TOTAL SOLIt'B
TOTAL DIBB. SOL I OB
TOTAL VOLATILE SOLIDS
VOLATILE DlSfl. SOLIDS
TOTAL VOL. SUB. SOL IDS
ANHONIA NITROOEN
TOC
DEHZENE
111 • 1-TR1CHLOROETHANE
CHLOROFORM
I,2-TRAN8-PICHLOROETHTLENE
ETHYLBENZEHE
HETHYLEHE CHLORIDE
TETRACMLOROETHYLEHE
TOLUENE
IRICHLOROETHYLENE
2r4'DlCHLOROPHEMOL
PHENOL
Ir2.4-IRICHLOROKCNZENC
Ir4 -DICHLOROBENZENE
|t2-PIPIIEHYLHYDRAZINE
FLUORANTHENE
NAPHTHALENE
OIS(2-ETHYLHEXYL> PHTHALATE
DI-N-BUTYL PHTHALATE
FLUOREHE
PHENANTHRENE
PYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
INFLUENT
77909
•7703
124*33
9303
399
261097
1*3394
12747?
49247
42412
407V
43228
9.7
2.9
24.1
.4
4.9
44. 9
4.9
40.8
2.4
1.2
41.2
N-P
M-D
1.4
N-0
9.3
.4
2.0
N-0
N-0
N-0
H-D
N-0
N-0
H-D
3?. 2
22.0
4.1
N-0
.2
N-0
2.4
0V. 7
TOTAL*
OUT
I120fl
i»38»9
1*4199
11019
7.2
3BI481
187949
147301
37263
130210
4700
f4472
,4
N-D
II. 0
N-D
L 0.1
11.7
.7
1.4
L O.I
.4
1.1
2.6
L O.I
N-P
.1
.2
N-D
N-P
L O.I
.1
L O.I
1.0
7.1
,8
l.»
144
39. 8
32.2
27.9
.4
43.3
8.7
179
EFFLUENT
4834
780*
I8SV3
last
4.8
177171
14*944
18473
32721
9f90
3347
10040
.4
H-D
10.4
N-D
N-P
IB. 4
.7
1.9
N-D
.4
,7
M-
N-
N-
H-
H-
N-
N-
H-
H-
N-
N-
N-
H-
N-
8
H-
21
N-
N-
f
1
N-0
.4
40.9
PRIMARY
SLUDGE
44*7
I2»»9
19827
I4»»
1.0
13744
700
•9*4
242
•744
22.9
3449
L O.I
N-P
L 0.1
N-0
I O.I
.1
L O.I
L 0.1
L O.I
H-D
.4
.4
L 0.1
N-0
.1
,2
H-D
N-P
L O.I
.1
L 0.1
L 0.1
1.0
L O.I
L 0.1
4.7
3.8
.4
2.7
L 0.1
3.7
.4
IS.O
SECONDARY
•LUDOE
100740
1730*1
141*39
8497
1.4
1*0344
17273
11*032
4118
119314
1331
82747
N-D
N-D
.4
N-P
N-P
N-P
N-D
N-P
N-P
N-P
N'D
2.2
N-0
N-D
N-0
N-0
N-P
H-D
N-P
N-D
N-0
1.0
4.1
.8
1.8
148
34.0
B.7
24.8
.4
3*. 4
7.*
11*
« TOTAL MASS OUT IS NO I ADJUSTED BY MASS CONTAINED IN REIURN FLOU8
POLLUTANTS NOT LISTED HERE NOT DETECTED 4T ANY SAMPLE POINT
L-LESB THANI N-P-NDT bEIECTED.
-------
MASS BALANCE IN FOUNDS PER DAY
FOR SAMPLE DATE INDINO BI0222 AT 0800 HOURS
FRACTION
HON-CONV. HE IAt8
PARAMETER
ALUMINUM
»AftIUN
IOROH
CALCIUH
CODALT
IRON
HAONESIUH
HANOANESE
80DIUH
VANADIUM
YTTRIUM
INFLUENT
TOIALI
OUT
EFFLUENT
129*
40,1
31.0
9.7
in*
2448
III
2773*
2.0
2.V
114
it.a
12.7
11221
3.7
lit
2231
•s.s
3f4U
N-B
N-D
•LUDOE
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
•ECONDARV
•LUDOE
NOT RUN
NOT RUN
HOI RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
( IOTAL MABB OUT IB NOT ADJUSTED DT MABS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L-LCSS THAN) N-D»NOT DETECTED.
-------
FRACTION
CONVEHTIONAL8
HOW-CONVENT IONAL 8
VOLATILEB
OJ
MASS BALANCE IN POUNDS fER DAY
FOR SAMPLE DATE ENDIN8 810223 AT 0800 HOURS
PARAMETER
DOD
TOTAL SUSP. SOLIDS
COD
OIL I OKEA8E
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIS8. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI88. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
BENZENE
1•1,I-TRICHLOROETHANE
CHLOROFORM
li2-TRANS-DlCHLOROETHrLENE
EIHVLBENZENE
HETHYLENE CHLORIDE
T E TKACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2f4-DICHLOROPIIEHOL
PENTACHLOROPHEHOL
PHENOL
l>2i4-TRICHLOROBENZCNE
1.4-DICHLORODEHZENE
fLUORANTHENE
DISI2-CHLOROETHYOXYI METHANE
NAPHTHALENE
D1BI2-ETHYLHEXYLI PHTHALATE
DI-N-IUTYL PHTHALATE
I.2-DEHZAHIHRACEHE
CHHYSENC
ACENAPHTHYtENE
FLUORENE
PHEHANTHMENE
PYRENE
ARSENIC
DCRVLLIUH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAH
MERCURY
NICKEL
* IOIAL MA9B OUI IS NOT APJIIBTED »Y MASS CONTAINED IN RE TUMI FLOWS
POUUTANTS HOI LISTCIi HERE NOT DETECTED AT ANY SAMPLE POINT
L-USS tll^M) N-f^NOr DETECTED.
ACID EXTRACT
BABE-NEUTRALS
METALS
INFLUENT
444*3
34*43
4788*
90*2
IB?
l***33
144971
3*743
I713f
22404
5771
44126
4.4
H-D
».2
• 3
7.1
7.1
4.1
47.5
3.4
N-D
M-D
74.7
N-D
N-D
H-D
2.7
3.4
4.1
N-P
H-D
H-D
H-D
H-D
N-D
H-D
H-D
N-D
N-D
0.8
S.fl
4.1
N-D
.1
H-D
TOTAL*
OUT
BS8S2
147484
314437
12740
4.4
302544
1330ft
1 28037
27338
100519
5402
1523fO
,3
1.2
4.0
N-D
L 0.1
4.2
.3
1.7
1.8
.3
.3
.3
.1
L O.I
3.0
H-D
.2
5.5
2.1
2.2
2,2
2.2
L O.I
L O.I
3.0
2.8
.3
2.f
127
31.3
8.7
14.3
L O.I
40.4
EFFLUENT
3034
3441
13»33
3*44
2.4
1235**
120138
28318
23444
4834
4351
»403
»
1.
5.
N-D
N-D
4,
,
1.
1.
f
.
* •
H-
H-
N-
N-
N-
3 3
2 I
H-
H-
N-
N-
N-
N-
N-
N-
N-
H-
N-
3 4
N-
N-
H<-D
PRIMARY
8LUDOE
4743
fB04
15377
4442
.8
10334
S3?
7054
273
4781
22. f
2841
L O.I
N-D
L O.I
N-D
L O.t
N-D
L O.I
.2
L O.I
N-D
N-D
N-D
.1
L O.I
.1
N-D
.2
H-D
N-D
N-D
N-D
L .1
L .1
L .1
L .1
t
L .1
L .1
1.
1.
,
.
L .1
.
SECONDARY
8LUDOE
78053
13221*
187123
4354
1.4
144413
143*4
*2483
33**
B88B«
828
140344
H-
H-
5
H-
N-
H-
N-
N-
H-
N-
H-
N-
»-
H-
2 *
N-
N-
N-
H-
2 2
3 2
2 2
N-
N-
3.9
2.7
.3
2.*
124
30.2
4.*
13.8
NiP
3V. 4
-------
HABB VALANCE IN POUNDS PER DAY
BAflFLE DATE ENIIIKO 8IO221 AT 0800 HOUR!
fKACIION
METALS
NOH-CONV. HE TALI
PARAMETER
SILVER
ZINC
ALUHIHUH
•AH I UN
tOROM
CALC1UH
CO ML I
IRON
MAGNESIUM
HANOANCSE
NOLVtDENUM
BODIUH
INFLUENT
.7
1008
32.1
30. a
(7112
2.7
984
2174
103
21.4
3JM3
TOTAL*
OUT
CrfLUENT
PRIMARY
SLUDUE
lECONDARr
ILUDOE
12*
13.1
• l.f
f.l
21.1
taut
i.o
72.1
1120
7i. f
N-»
22430
.1
.4
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
MOT RUN
HOI RUM
4.7
112
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
HOI RUN
HOI RUM
•P-
-P-
I TOTAL MASS OUT IS NOT ADJUSTED BY NABS CONTAINED IN BE IURN FLOUB
POLLUTANTS NOT LISTED MERE NOT DETECTED AT ANY SAHPLE POINT
L'LESS THAN* H-»'NOT DETECTED.
-------
FRACTION
COHVEHTIOHALB
NON-CONVENT IONALS
PARAMETER
POD
TOTAL SUSP
COD
OIL I OREABE
MASS BALANCE IN POUNDS PER DAY
FOR SAMPLE HATE ENDIHO 810224 AT 0800 HOURS
SOLIDS
ACID EXTRACT
BABE-NEUTRALS
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DISB. BOLID8
TOTAL VOLATILE SOLIDS
VOLATILE D1SS. SOLIDS
TOTAL VOL. SUB. SOLIDS
AMMONIA N1TROOEN
TOC
VOLATILES BENZENE
I.1•1-TRICHLOROETHANE
It1•2-TRICHLOROETHANE
CHLOROFORM
ETHTLDEHZEHE
HETHTLENE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TftlCHLOROETHVLENE
2>4-DIHITROPHEHOL
PHENOL
ACENAPHTHENE
1.2.4-TRICHLOROBENZENE
I<2-DICHLOROBENZENE
Ifl-DICHLORODCHZENE
I*4-PICHLOROBENZENE
FLUORANTNENE
NAPHTHALENE
PI8«2-ETHYLHEXrL) PHTHALATE
DI-N-PUTVL PHTHALATE
1,2-BEHZAHTHRACENC
llil2-BENZOFLUORANTHENE
CHRTBENE
ANTHRACENE
FLUORENE
PHENANTHRENE
PYRENE
METALB ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
* TOTAL HA8B OUT IB NOT ADJUSTED PY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-IE83 THAN) N-D-NOT I'ETECTEIi,
INFLUENT
118*17
*223I
23724*
7207
113
4*3487
3****9
118997
42702
33B39
3403
100*00
4.3
3.8
N-D
28.8
1.8
13.0
17.7
82.*
»0.1
1.4
44.*
104
14.2
N-D
1.4
2.9
N-0
7.2
1.4
1.4
N-P
N-P
N-D
N-D
.7
H-P
H-P
4,0
H-D
N-D
I.B
82.9
44.8
32.4
TOTAL*
OUT
131011
197438
282343
11377
13.2
4*7377
3000*3
139843
27304
1324*8
3*33
84084
1.0
1.0
I O.I
*.3
.4
23.0
2.4
3.8
(.4
H-D
2.4
N-D
9.8
L O.I
.4
,2
.3
.4
N-D
N-D
L O.I
L O.I
L 0.1
.2
L O.I
.2
.2
1.7
11.7
.9
3.3
194
34.4
24.9
EFFLUENT
9724
7437
33442
N-D
11.3
273304
243847
24383
224*4
38*0
3187
19342
1.
1.
H-D
*.
t
23.
2.
3.
1,
N-D
2.4
N-D
2.3
H-D
.4
N-D
H-D
H-D
H-D
H-D
H-D
H-D
H-D
H-D
H-D
N-D
H-D
1.4
4.2
N-D
H-D
*<7
8.4
13.0
PRII
SLUI
133;
14*
l»»1
*4I
,;
ISO'
114
9821
2*2
*4*4
28.:
3741
L (
L (
L <
L <
L <
H-D
L <
L <
N-D
N-P
N-D
1.
L
N-D
,
,
i
H-P
N-P
L
L
L
.
L
.
•
L
1.
L
L
7.
1 .
,
IARV SECONDARY
>OE SLUDOE
IB 107*37
0 1730*1
>2 22470*
10434
' 3.2
P4 204197
33107
» 123431
4318
t 119112
1 720
1 44774
1 N-D
> N-P
I H-D
» N-D
> N-D
N-D
I.I N-D
I N-D
1.1 N-D
N-P
H-P
H-D
2.3
.1 H-D
H-D
H-P
N-D
H-D
N-P
H-P
.1 H-P
.1 H-P
.1 H-P
H-P
.1 H-P
H-P
H-D
.1 N-D
1.4
.1 .3
.1 1.2
174
44.8
10.7
-------
MASS BALANCE IN POUNDS PER VAT
FDR SAMPLE PATE CNPINO 810224 AT 0800 HOURS
FRACTION
HETALS
NUH-CONV. HCTALB
PARAMETER
LEAP
MERCURY
NICKEL
SELENIUM
SILVER
ZINC
ALUHINUH
BARIUN
BORON
CALCIUM
COBALT
IRON
HAONESIUH
HANOANESE
HOIYBDENUH
BOBIUH
TITANIUN
VANADIUM
YTTRIUM
INFLUENT
N-0
.1
33.8
N-P
2.2
202
2180
90,4
90,4
IfOf*
B.I
973
2BB1
121
14.1
1141*3
23.B
1.8
3.*
TOTAL*
OUT
10,f
L O.t
98.2
L 0,1
B.I
EFFLUENT
U.2
N-B
22.7
N-D
.1
33.7
10
».7
27.*
1*210
9.9
107
23f4
71.)
20,1
7*312
N-B
N-B
N-B
PRIMARY
SLUDOE
.7
L 0.1
.*
L O.I
.2
1. 7
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
8LUPOE
22.0
N-D
34, t
N-P
7.4
138
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
* TOTAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOU8
POLLUTAMTU NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L»LESS THAMI N-O'NOT DETECTED.
-------
NABB KEIURNED 10 PLANT IN FOUNDS PER PAY
fOK BAHFLt UA1E E Mil I HO B10224 AT OBOO HOURS
FRACTION
CONVENTIONALS
NON-CONVENTIONALB
PARAMETER
BOD
TOTAL SUSP.
COD
OIL I OREAIt
SOLIDA
V
-p-
VOI.ATILES
ACID EXTRACT
BASE-NEUTRALS
HETALS
NIIN-CONV. HETAI.6
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOI ITS
TOTAL VOLATILE SOLIDS
VOLATILE PIBS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROGEN
TOC
BENZENE
CHLOftOBENZENE
Ii2-TRANS-DlCHLOftDETHfLENE
ETHYLBENtEHE
HETHTLCNC CHLORIDE
TOLUENE
PHENOL
ACENAPMIHENE
lt)-DICHLORdtENZENE
l»4-t>tCHLOROBEH2ENE
BISI2-CMLOROETHYOXY) METHANE
NAPHTHALENE
BIB(2-ETHYLHEXYL> PHTHALATE
DI-N-SUTTL PHTHALATE
BI-N-OCTYL PHTHALATE
DIMHTL PHTHALATE
ACEHAPHTHYLENE
ANTHRACENE
I,I2-»ENZOPERTLENE
PHENAHTIIREHE
l»2t9l4-MkENZANTHRACEHE
ARSENIC
BERYLLIUM
CAHNIUN
CHROMIUH
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
DIGEST
SUPCRN
271
1028
ll»l
130
.4
244*
1440
7BB
321
4«8
141
471
L O.I
L O.I
L O.I
,2
L O.I
,1
N-D
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
N-D
L 0.
L 0.
I 0.
L 0.
L 0.
L 0.
L 0.
.5
.3
L 0.
,3
L 0.
.3
L 0.
1.2
23.9
.3
ER VACUUM FILTER
ATANT FILTRATE
27. S
48.7
77. S
1.2
L O.I
380
310
42.9
33.0
7.S
12. S
23.7
L 0.1
N-D
N-D
L O.I
L O.I
L 0.1
L O.I
N-0
N-B
N-D
L 0.1
N-D
L 0.1
N-D
N-D
L O.i
L 0.1
N-D
H-D
H-D
H-D
N-D
N-D
N-D
L 0.1
L O.I
1 N-D
N-D
1 N-D
L 0.1
1 L 0.1
L 0.1
.4
L O.I
TOTAL MASS
RETURNED
2?B
10?4
124V
131
.7
284V
1790
831
194
479
191
499
L O.I
L 0.
L 0.
.2
L 0.
.1
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
.9
.1
L O.I
,3
L O.I
.3
L O.I
1.2
24.4
.4
F-nllUTANTS HOI L1BIED UEKE NOT DETECTE.D AT ANY SAMPLE POINT
L-LESS THANI H-D-NOT !>EUCTEB.
-------
MASS RETURNED TO fLANT IN FOUNDS PER DAY
FOR BANPIE DATE ENDINO BI0224 AT OBOO HOUR!
FKACTIOH
NOH-CONV. HUMS
PARAMETER
fcORON
CALCIUM
CO*ALT
IRON
HAONEBIUN
MANOANCSC
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
YTTRIUM
DIGESTER VACUUM FILTER TOTAL HAH
SUPERNATANT FILTRATE RETURNED
,2
324
L 0.1
17.1
42.2
3.7
L 0,1
298
L 0.1
L O.I
.2
L O.I
«7.9
L 0.1
I.I
».o
.«
N-fi
34.3
L 0.1
N-D
L 0,1
.2
J»l
L,
16.
31.
4.
L
314
L
L
.1
.1
.1
,1
.2
7
00
POLIUTANI8 NOT LISTED MERE NOT DETECTED AT ANY SAMFLE POINT
I.-LESS THANI H-D-NOI DETECTED.
-------
MASS DALANCE IN POUNDS PER DAY
FOR SAMPLE DATE ENDIHO 810223 AT 0800 HOURS
FRACTION
CONVENTIONALB
NON-COHVENTIOHALB
VOLATILEB
ACID EXTRACT
BASE-NEUTRALS
PARAMETER
BOD
TOTAL SUSP. BOLID8
COO
OIL I OREABE
TOTAL PHENOL B
TOTAL BOLIDB
TOTAL DIBB. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBB. SOLIDS
TOTAL VOL. SUB. BOLIDB
AMMOMtA NITROOCN
TOC
BENZENE
I r I i I -TRICHLOROE THANE
1.1. 2-TRICHLORDETHAHC
CHLOROETHANE
CHLOROFORM
ETHrLBENZCHE
HETHTLENE CHLORIDE
TETRACHLOROETHYLCNE
TOLUENE
TftlCHLOROETHYLENE
2>4-DINITROPHENOL
PCNTACHLOROPtlENOL
PHENOL
ACENAPHTHEHE
l»2r4-TRICHLOROBENZEHC
I>3~DICHLORO*ENZENE
li4-DICHLOROBENZENE
FLUOR ANTHEHE
DIB(2-CMLOROETHYOXY) METHANE
NAPHTHALENE
DIB(2-ETHYLHEXYL> PHTIlALATE
BUTYL BENZYL PHTHAI.ATE
t't-M-IUTTL PHTHALATE
DUTH'L PHTHALATE
FLUORENt
FHEMANTIOVENE
Al IHONY
ARSENIC
DCRYLLIUH
METALS
CHROMIUM
COPPER
CTANIliC
LEAD
« TOIAL MASS OUT IS MOT ADJUSTED Cr MASS CONTAINED IN RETURN FLOUB
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
L»LESB IHANI N-D-NOf DEUC1ED.
INFLUENT
121034
74875
242393
• 437
244
4I83U
3444f3
120973
7733*
43238
3? 74
94470
21.1
2. a
N*D
N-0
31.*
22.1
3.3
22. B
VI. 4
13.0
1.1
2.1
38.7
77.3
14.2
.7
l.B
N-0
11. A
t.l
1.4
N-D
2.8
4.0
.7
N~D
3.V
N-0
N-0
2.S
3B.7
33.2
24.4
17.4
TOTAL*
OUT
121231
1*2130
34417t
17538
24.4
941423
348921
1443fl
29339
133121
4370
137894
1.4
M-0
,t
.7
10.7
2.4
8.9
3.2
».2
1*.2
N-0
N-0
2.1
H-D
10.4
.4
M-0
.1
1.3
.3
.2
.1
N-D
a. s
N-0
.1
1.9
3.4
L 0.1
1.9
77.1
14,7
23.4
1.3
EFFLUENT
17494
12412
54732
1974
20. S
321994
30B334
31329
21440
10009
3783
24908
1.4
N-0
N-D
N-D
10.1
1.9
e.s
2.8
8.2
18.3
N-0
N-0
1.4
N-D
4.4
.4
N-D
N-0
1.3
N-D
N-D
N-D
N-0
8.3
N-D
N-D
1.9
N-D
N-D
N-D
9.1
9.1
10.7
N-D
PRIMARY
SLUDBE
13411
19884
80718
3387
.7
42298
2422
27044
401
24431
II. 1
13827
N-D
N-0
.3
N-0
L 0.1
i 0.1
N-0
N-D
N-B
.4
N-D
M-0
.3
N-D
1.9
N-D
N-D
.1
H-D
.3
.2
. |
N-D
N-D
N-D
.1
N-D
.7
L 0.1
.1
10.4
2.2
3.7
1.3
SECONDARY
SLVDBE
89944
139424
224709
12999
9.4
177749
38143
109798
7197
98401
974
97141
N-P
N-D
.3
.1
.3
.4
N-D
.4
1.0
.9
N-D
N-D
N-D
N-D
4.3
H-D
N-D
N-D
N-D
N-D
H-D
N-D
H-D
H-D
N-D
N-0
H-D
2.7
L 0.1
1.8
37.4
3.4
7.2
N-l»
-------
MASS BALANCE IN FOUNDS flK PAY
FOR SAMPLE DATE EHPINO 010229 At OttOO HOURS
FKACI10N
HE1ALB
WJN-CONV. METALS
O
I
PARAMETER
HERCURY
NICKEL
SILVER
ZINC
ALUMINUM
iAftIUN
ftORON
CALCIUM
COMLT
IKON
MAGNESIUM
MAMOANEBE
HOLV»l»EN.Un
SODIUM
IIIAMIUM
VANADIUM
INFLUENT
TOIAL*
OUT
N-0
20.7
2.1
110
1350
IB.7
92.7
1B27T
8.4
749
1141
102
7.4
»213I
*.I
2.1
L O.I
40.4
1.2
7*.2
EFFLUENT
N-0
IB. 4
.3
34. a
177
11.4
30.3
14060
4.4
147
2322
73.7
4.0
?447»
N-D
N-D
PRIMARY
SLUDGE
L O.I
I.I
.2
11.2
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
IECONDARV
BLUDOC
N-0
20. 9
.7
11.2
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
« TOTAL MASS OUT IS NOT AlUUSICb 6r MASS CONTAINED IN RETURN FLOWS
PUILUTANTS NOT LISTED UEKE HOI PETECTCD AT ANY SAMPLE POINT
L'LESS THANI N-II-NIH liEUCIEH.
-------
MASS BALANCE IN POUNDS ft ft PAY
FRACTION
CONVENTIONALB
PARAMETER
BOD
TOTAL SUSP
COD
OtL I DREA9E
FOR BAHPLE DATE ENDINO 610224 AT OBOO HOURS
SOLIDS
HON-CONVENTIONALB
VDLATILE8
Ul
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. BOLIDB
TOTAL VOL. BUS. SOLIDS
AHHONIA NITROOEN
TOC
BENZENE
Ii1t2-TRICMLOROETHANE
CHLOROFORM
ETHYLDENZENE
METHYLCNE CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2>4,4-TRICHLOROPHENOL
2-CHLOROPHENOL
2>4-DICHLOROPHENOL
2,4-DIMETHYLPHEMOL
2-NITROPHENOL
PHENOL
ACENAPHTHENC
l>2r4-TRICHLOROBENZENE
l»3-DICtllOROBENZENE
1.4-D1CHLOROBENZENE
NAPHTHALENE
DIB(2-ETHYLHEXYL> PHTHALATE
DI-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
ACENAPHTHYLENE
PHENANTHRENE
ARSENIC
•ERVLLIUH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
* TOTAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOVS
POLLUTANTS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
L-IESB THANI N-D-NOT DETECTED.
ACID EXTRACT
BABE-NEUTRALB
METALB
INFLUENT
I1B443
79994
2S77B7
11MB
101
449383
3727 it
101171
34434
449J9
73U
7B3BI
3.8
N-D
29. 4
B.O
7.3
II. I
41. 8
14.7
N-D
H-D
H-D
N-D
H-D
44.2
.7
31.7
2.1
9.2
N-D
4.9
4.2
2.4
N-D
N-D
N-D
N-D
N-D
24,4
28.9
24.1
22.3
.2
29.3
2.B
TOTAL*
OUT
.
230B94
409347
17420
49,9
407744
394943
227914
38733
148844
4484
430481
1.2
.2
.7
.4
.1
.4
.3
.4
.3
.3
.4
4.4
.9
21.2
N-D
19.9
N-D
2.4
.4
,3
N-D
2.2
.4
.2
*.9
.9
3.4
189
72.3
IV. 8
29.0
L O.I
40.2
7.B
EFFLUENT
NOT RUN
34022
48447
N-D
3».0
333822
321489
49404
92437
J7I47
4038
90292
1.2
N-D
8.7
1.2
8.1
.9
4.9
3.4
.3
.3
.4
4.4
.9
21.2
H-D
19.0
N-D
2.3
N-D
N-D
N-D
2.2
.4
N-D
N-D
N-D
N-D
13.7
13.1
9.7
N-D
N-D
18.7
1 ,4
PR I NARY
BLUDOE
30071
27330
74387
3909
2.8
29913
2327
17948
93B
17093
92.2
20S79
L .1
4
L . ,1
L .1
L .1
4
,
9
N-P
N-D
N-D
N-D
N-D
N-D
N-D
1.9
N-D
.1
,4
.3
N-D
N-0
N-D
.2
.2
.1
.9
98.4
30.1
2.0
9.2
L O.I
17.4
.0
SECONDARY
SLUDOE
I3B337
189284
244293
13711
B.I
222031
32747
140344
9798
134984
974
399834
H-D
N-D
.9
.1
N-D
.4
1.2
N-D
H-D
N-D
N-D
N-D
N-0
N-D
H-D
2.4
N-D
N-D
N-D
N-D
N"D
N-D
N-D
N-D
4.7
.4
2.9
112
29.1
B.I
19.8
N-D
24. t
9.4
-------
MASS HALAHCE IN FOUNDS flit PAY
FOR SAMPLE DATE ENDIMO 010224 AT OBOO HOURS
FRACTION
MEIALB
NON-COMV. ME1AL8
?
Ul
PARAMETER
1INC
ALUMINUM
•ARIUH
»OROH
CALCIUM
COHALT
IKON
HAONEBIUH
HANOANE8E:,
MOLYBDENUM
•ODIUM
TITANIUM
VANADIUM
INFLUENT
»7.S
1 84 A
48. B
53.7
177*4
1.8
1087
HIS
103
9.2
TOTAL!
OUT
341
8.7
1.1
EFFLUENT
42.4
877
23.6
40,4
19*18
4.4
481'
380V
81.3
4.1
»0204
9.4
N-D
PRIMARY
BLUPBC
142
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
ILUDOE
117
NOT RUN
NOT RUM
MOT RUN
NOT RUN
NOT RUN
HOI RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
* lOfAL MASS OU1 18 NOt ADJUSTED PY MASS CONTAINED IN MIUKN FLOWS
POLLUTANTS NOT LISTED UEKE NOT DETECTED AT ANT SAMPLE POINT
L-LESS THANI N-U-NOT DETECIEV.
-------
MASS BALANCE IN FOUNDS PER HAY
TRACT IOH
CONVENTIOHALS
NON-CONVENT IONAL8
VOLATILES
Ul
LJ
ACID EXIKACT
BASE-NEUTRALS
PARAMETER
>OD
TOTAL SUSP
COP
OIL I CREASE
FOR SAMPLE DATE EMM NO 01022? AT 0800 HOURS
SOL IUS
TOTAL PHENOLS
TOTAL 8011 PS
TOTAL PISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE MBS. SOLIDS
TOTAL VOL. SUB. SOLIDS
AMMONIA NITROGEN
TOC
BENZENE
CHLOftOBENZENE
lilil-TRICHLOROETHAHE
Itt-DICHLOROETHANE
lrlt2-TRICHLOROETHANE
!>Ii2i2-TETRACHLOROETHAME
CHLOROFORH
1.2-TRANB-PICHLOROETHYLENE
|i3-DICHLORQPROPYL£NE
ETHYLBENZENE
HEtHVLENE CHLORIDE
CMLORODISROHOHETHANE
TETRACHLOROETIIYLENE
TOLUENE
TRICHLOROETHYLENC
2>4>4-TRICHLOROPHEHOL
2r4-DICHLOROPHENOL
PHENOL
ACENAPIITHENC
1>2.4-TRICHLOROBENZEHE
{•2-DICHLOROBENZENE
1.3-DICHLOROBENZCNE
I»4-DICHLOROBENZENE
FLUORANTHENE
NAPHTHALENE
BI8(2-EIHYLHEXYL> PHTHALATE
BUTYL BENZYL PHTHALATE
DI-N-BUTVL PHTHALATE
D1ETHYL PHTHALATE
112-BENZANTHRACENE
ANTHRACENE
FLUOfcENE
PHENAMTHftENE
PYftENE
INFLUENT
133333
83902
243419
13333
240
441788
377234
IS2S20
93008
5fSI2
S203
1 1 9479
9.2
2.
3.
1.
t
I.
48 1
1.
t
f.
14.
9
13.
B4.4
S.S
N-D
H-B
28.0
N-D
14.9
N-D
1.3
4.2
3.4
N-B
N-D
N-D
21. B
5.?
19.2
2.0
1.3
2.0
2.9
TOTAL*
OUT
1 43734
244840
923144
29292
91.0
419749
394890
292103
93319
I987B9
3997
» 14084
,9
H-D
.3
H-D
L 0.1
N-D
14.3
H-D
N-D
1.7
21.4
H-D
1.0
12.9
.4
.3
.9
2.3
12.9
13.1
.2
1.4
.1
.2
3.6
21.3
L O.I
1.7
10.7
N-D
L O.I
L 0.1
.2
.2
EFFLUENT
21399
14432
40413
1443
39.0
329043
314412
97270
84013
11297
2884
28284
.9
H-D
.3
N-D
H-D
N-D
13.3
N-D
N-D
1.2
21.4
N-D
.4
10.1
.3
.3
.9
1.7
12.4
4.0
H-D
1.4
N-D
N-D
N-D
2.3
N-D
1.7
10.7
N-D
N-D
N-D
N-D
N-P
PRIMARY
SLUDGE
12820
20100
102873
9440
2.9
22433
3433
12944
449
12282
98.4
19827
L O.I
N-D
H-D
N-D
L O.I
N-D
.2
N-D
H-D
L 0.1
N-D
N-D
L 0.1
.4
.1
H-D
H-D
.4
L O.I
2.8
,2
H-D
.1
.2
.9
22.2
L O.t
N-D
N-D
N-D
L O.I
L 0.1
.2
.2
SECONDARY
SLUDOE
I1I99S
230308
399894
18389
9.9
248093
37783
182087
4837
173290
412
71971
N-D
N-P
H-D
N-D
H-D
N-D
1.0
H-D
N-D
.4
H-D
N-D
.3
1.8
H-D
N-D
H-D
H-D
N-D
8.3
H-D
H-D
H-D
H-D
2.9
N-D
N-D
N-D
H-0
H-D
N-D
H-D
N-D
N-D
» TOTAL HASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOUB
POLLUTANTS NOT LISTED WIRE NOT DEFECTED AT ANY SAMPLE POINT
I-I ESS THANI H-P-MOT HETECTED.
-------
(IAS8 VALANCE IN POUNDS PER I'AT
FOR SAMPLE DATE EMUINO 010327 AT 0800 HOURS
FRAC 11ON
HETA1S
NON-COHV. HCTALS
O
PARAMETER
ARSENIC
•ERYLLIUM
CADHIUH
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
•ARIUH
IDkON
CALCIUM
COkALT
I ROM
HAOHE8IUH
HANOANESE
HOLVkDENUH
SODIUM
TITANIUM
VANADIUM
YTTRIUM
INFLUENT
N-0
.7
N-D
38.3
28. 4
20.5
N-D
.1
28. 0
2.3
84. «
2083
43,3
33.3
142*0
4.2
747
2*27
87.1
tt-D
»asi7
V.I
1.4
20.2
TOTAL*
OUT
17. »
.3
1.1
1S3
4». 2
37.3
31.0
L O.I
30.3
».«
m
_
-
-
-
-
-
-
-
_
-
-
•
-
EFFLUENT
H-8
N-D
N-D
3.3
N-D
24.0
N-D
N-D
I*. 3
.1
28.1
141
f.2
14. 1
13344
9.2
ISA
23f8
37.7
2.9
»i2oa
N-D
N-D
N-D
PRIMARY
BLUIieC
.8
L O.I
.2
10.4
«.o
1.7
4.*
L O.I
2.8
.8
20.4
NO! RUM
NOT RUN
HOT RUM
NOT RUN
NOT RUN'
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
8LUDOE
U.2
.4
2,1
140
43.2
11.4
28.4
N-D
28.4
a. 3
144
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
« IUIAL MASS OUT IS NOT ADJUSTED DY MASS CONTAINED IN RETURN FLOU8
POILUTAMTS NOT LlflttD UEkE NOT DETECTED AT ANY SAMPLE POINT
I.-LESS THAN! N-II-NOI DETECTED.
-------
MASS BALANCE IN IOUNP8 PER DAY
FRACTION
CCINVENTIONALB
NON-CONVENTIONAL8
PARAMETER
»OD
TOTAL SUBP
COD
OIL I CREASE
FOR SAMPLE DATE ENDING 810228 AT 0900 HOURS
SOLIDS
m
Ul
VOLAT1LES
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. SUB. 30L108
AHNONIA NITROOEM
TOC
BENZENE
1* Irl-TRICHLOROETHANE
1rI>2-TRlCHLOROETHANC
CHLOROFORM
112-TRANS-DICIILOROETHYLENE
ETHTLBENZENE
HETHYLEME CHLORIDE
IE1RACHLOROETHYLENE
TOLUENE
1RICHLOROETHYLCNE
2.4.4-IRICHLOROPHENOL
J, 4~DI«Etim PHENOL
PHENOL
ACENAPHTHEME
1.2f4-TRICHLOROBENZENE
112-MCHLOROBENZENE
1.3-DICHIOROBENZENE
I , 4-DICHLOROBENZENE
FLUORAMTHENE
NAPHTHALENE
BIS<2-ETHYLHEXYL> PHTHALATE
DI-N-VUTYL FHTHAIATE
DI-N-OCTYL PHTHALATE
DIETIIYL PHTHALATE
DIMETHYL PHTHALATE
CMRYSENE
ANTHRACENE
FLUORENE
PHENANTHRENE
PYRENE
ANTIMONY
ARSENIC
BERYtLIUH
CADMIUM
I TOTAL HASH OUT IB NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOWS
rnilllTANTS NUT LISTFb KEKE NOT DETECTED AT ANY SAMPLE POINT
L-IESS IMANI N-P-NGT DETECTED.
ACID EXTRACT
BABE-NEUTRALS
METALS
INFLUENT
8IB90
81890
20*274
4976
227
370020
286917
120109
72104
47*21
3743
74307
3.0
i.a
H-D
28.8
1.2
10. 9
HOT RUN
10.4
73. S
1.3
N-D
5.3
33.4
N-D
17.3
H-D
2.4
10. A
.3
N-D
10. r
2.7
2.1
9.8
S.2
.A
l.S
3.6
l.S
2.1
3. A
3.9
N-D
M-I»
TOTAL*
OUT
42494
33414?
334484
23B72
49.3
814734
460*72
384237
118868
247322
1408
103720
.8
.3
L 0.1
10.6
N-D
.4
12, 8
.6
19.4
L 0.1
.3
2.1
2.9
.3
10.7
.3
.3
2.9
.2
4.0
203
3.1
.3
3.7
3.3
N-D
N-D
.3
.1
.2
L 0,1
9.4
.3
2.3
EFFLUENT
1669
12813
42714
1333
34.7
432902
419131
II 8804
108924
9B7B
2937
18933
.8
.3
H-D
9.6
M-D
N-D
12.8
.3
13.3
N-D
.3
2.1
2.4
.3
4.0
N-D
.3
2.9
N-D
M-D
1.3
S.I
N-D
3.7
3.3
N-D
N-D
,3
N-D
N-D
N-D
N-D
N-D
N-D
PRIMARY
BLUDOE
6647
48272
40143
4234
2.2
30644
2299
28489
384
27834
38.4
11399
L O.I
N-D
t O.I
.2
H-D
L O.I
L O.I
.1
.7
L 0.1
N-D
H-D
.3
H-D
1.3
,3
N-D
H-D
.2
.9
7.4
H-D
.3
N-D
N-D
N-D
N-D
N-D
.1
.2
L O.I
1.7
L O.I
.1
SECONDARY
SLUDGE
33978
293002
41IB27
16301
e.6
333386
39224
238944
9334
229388
412
73370
N-D
N-D
M-D
.8
H-D
.3
H-D
N-D
1.4
H-D
N-D
N-D
M-D
M-D
3,4
N-D
H-D
H-D
M-D
3.1
194
H-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
7.»
.3
2.2
-------
MASS DALAHCE IN POUNDS PER DAY
FOR SAMPLE PATE ENblNO B1072B AT 0800 HOURS
FRACTION
METALS
NON-CONV. HE IALB
Ln
ON
PARAMETER
CHROMIUM
COPPER
CYANIDC
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
»ARIUN
•OkON
CALCIUM
CODALT
IRON
HAONEBIUH
HANOAHEBE
BODIUH
TITANIUM
VANADIUM
INFLUENT
TOTAL!
OUT
130
2B.2
93.7
N-D
.2
20,0
t.a
97.1
28 VO
49.9
31.4
14998
9.9
1204
2730
100
B0371
11.2
2.1
130
44.2
171
18.1
L O.t
44.3
7.B
172
EFFLUENT
9.4
1.3
HI
19.2
N~ft
14.3
.3
20.8
PR IN ART
8LUDOE
II. 1
9.1
l.t
3.B
L 0.1
2.7
.7
20. 4
107
4.4
29.4
I20M
2.1
117
2134
90.7
7B224
H-0
H-D
NOT RUN
HOI RUN
HOI RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
•ECONPAftY
ILUDOE
133
39.4
• .9
I*.I
N-D
27.3
4.0
130
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
* TOTAL MASS OUI IS NOT ADJUSTED BY MASS CONTAINED IN RETURN fLOUB
POUUIANI8 NOT LISTED UEKE HOI DETECTED AT ANY SAMPLE POINT
L-LESS THAN) N-D*NOI DETECTED.
-------
MOSS PALANCE IN POUNDS PEA HAY
FOR SAHPLE ['ATE CMC'INO BI030I At 0800 HOURS
FRACTION
CONVENTIONALS
NON-CONVENTIONAL8
I
(Jl
VOLATILES
PARAMETER
HOD
IOTAL SUSP. SOLIDS
COO
OIL I GREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIS9. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. SUS. SOLIDS
AMMONIA NITROGEN
TUG
BENZENE
1 • 1 • 1-TRtCHLOROETHANE
1,1,2-TKlCHLOftOETHAME
CHLOROFORM
I » 1 -HICHLOROETHYLENE
11 2-D1CHLOROPROFANE
ETHYLBEN2EHC
HETHYLENE CHLORIDE
METHYL CHLORIDE
TETRACHLOROETHYLENE
TOLUENE
TRICHLQROETHTLENE
2.4-DICm.OROPKENOL
2.4-lHHETHYLPHENOL
ACENAPHIHENE
I»2i4-TRtCHLOROBENZENE
ACIH EXTRACT
BASE-NEUTRALS
I>4-DICHLOROBEHZENE
1>2-DIPHENYLHYDRAZINE
FLUORANTHENE
NAPHTHALENE
H-NITROSODI-H-PROPYLAHINE
BISI2-ETHYLHEXYLI PHTHALATE
DI-N-BUTYL PHIHALATC
DIETMU PHTHALATE
CHRYSENE
ANTHRACENE
FLUORENE
PHEHAHTHRENE
PYRENE
NEIALB ANTIMONY
ARSENIC
PCRYLI 1UM
CADMIUM
I TOTAL MASS OUT IS NOT ADJUSTED BY HAS8 CONTAINED IN RETURN FLOU6
foil UIAH IS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L^LESS 111 AH I N-D'NOT DETECTED.
INFLUENT
103704
8S4B8
142422
3332
233
330424
240392
104733
92078
94434
4449
41679
3.1
1.0
N-D
N-D
13.9
,3
M-D
1.1
90.2
4.4
47.0
34.1
1,8
1.8
N-D
7.2
.8
3.1
.3
3.1
H-0
7.2
11,9
4.4
3.4
t.O
1.0
1.3
1.0
2.8
H-D
3.4
H-D
H-D
TOTAL*
OUT
194232
434944
333332
17344
37.3
496428
242769
394340
30899
343409
3744
39244
.4
N-D
.1
9.0
H-D
H-D
1.0
10.7
N-D
L O.I
4.2
.4
H-J»
2,7
L 0>1
11.7
2.4
H-D
H-D
.2
2.7
H-D
1.6
N-D
3.B
H-D
H-D
,2
,1
.1
3.4
4.0
.4
2.8
EFFLUENT
7977
5539
24369
1994
24.4
2140)6
210499
29470
23240
4210
3102
11922
.4
H-D
H-D
4.9
N-0
W-D
.9
10,4
N-0
H-D
3,3
.4
N-D
2.7
N-D
4.4
2.4
H-D
N-D
N-P
H-D
N-D
1.6
N-0
3.8
H-D
N-D
.2
H-D
H-D
H-D
N-D
N-D
N-D
PRIMARY
SLUDOC
4746
44790
41130
2437
2.B
47144
2422
23007
401
24374
44.3
2S32
N-D
N-D
.1
.1
N-D
N-D
L O.I
L O.I
H-D
L O.I
.7
.2
N-P
N-D
L 0,1
1.0
H-D
H-D
H-D
.2
.3
H-D
H-D
N-D
N-D
H-D
H-D
N-D
.1
.1
,3
2.4
L O.I
.3
SECONDARY
SLUDOE
1B3327
404437
447813
J3I33
8,1
433424
29648
341843
3038
334623
374
23190
H-D
N-D
N-D
H-D
H-D
H-B
H-D
H-D
N-0
H-D
H-D
H-D
N-D
H-D
N-0
4.3
N-D
N-D
N-D
H-D
2.2
H-D
H-0
H-D
N-D
N-D
H-D
N-D
H-D
N-D
2.9
3.4
,3
2.3
-------
MASS VALANCE IN POUNDS PER OAT
FOR SAMPLE DATE EMDINO BI010I AT 0800 HOURS
FRACTION
HEIALB
NOH-CONV. METALS
7
U1
00
PARAMETER
CHROMIUM
COPPER
CYANIDE
IEAD
MERCURY
MICHEL
SELENIUM
SILVER
ZINC
ALUHINUM
DARIUN
fcORON
CALCIUM
CODALT
IRON
HAONEBIUM
HANOANESE
MOLYBDENUM
SODIUM
TITANIUM
VANADIUM
INFLUENT
TOTAL*
OUT
12.4
14.7
8.9
19.7
L 0.1
N-D
N-D
1.0
31.4
41B1
11.9
14.1
11444
1.1
1103
2578
12*
N-D
74099
14.2
2.3
134
41.0
47.1
10.7
.1
31.1
.1
8.7
172
EFFLUENT
N-P
10.2
17.7
N-0
L O.I
N-B
H-D
N-D
12.*
39.
4.
28.
ff7
a.
•4.
1773
4*. 7
3,7
9*141
N-0
N-D
PHI HART
•LUDOE
30.1
11.2
1,
4.
L .1
4,
1
1,
I*.
NOI RUN
HOT RUN
NOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
tLUDOE
i»4
If .4
7.1
24. t
N-0
2».l
N-0
7.4
lit
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUH
HOT RUH
* IOIAL MASS OUI IS NOT ADJUSTED »Y MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED WERE NOI DETECTED AT ANY SAMPLE POINT
L-I.EES THAN* N-D-NOI DETECTED.
-------
FRACTION
CONVENTIONAL8
NON-CONVENT IONALS
7
Ul
VOLAI1LES
MASS BALANCE IN POUNDS PER DAT
FOR SAMPLE HATE END1NO 810302 AT 0800 HOURS
PARAMETER
BOD
TOTAL SUSP. SOLIDS
COD
OIL t OREA8E
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL MBS. SOLIDS
TOTAL VOLATILE SOLIDB
VOLATILE DISS. SOLIDS
TOTAL VOL. SUS. SOLIDS
AHMOHIA NITROOEH
TOC
BENZENE
CMLOROBENZENE
Irltl-TRICHLOROEIHANE
CHLOROFORM
ETHVLBENZENE
HETHYLEHE CHLORIDE
TC1RACHLOROETHYLENE
TOLUENE
TRICHLOROETHYLENE
2>4-DICHLOROPHCHOL
PHENOL
ACCHAFHTHENE
lr2i4-TRICHLORO»EN2EHE
1»2-DICHLOROBENZENE
If3-DICHLOROIENZENE
tft-DICHLORORENZENE
FLUOftANTHENE
NAPHTHALENE
BIS(2-ETHYLHEXYL> PHTHALATE
BUTYL BENZYL PHTNALATE
Dl-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
!>2-BENZANTHRACENE
CHRYSENE
ANTHRACENE
FLUORENE
PHENANTHRENE
PYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
• TOTAL MASS OUT IS NOT AI'JUSTED BY MASS CONTAINED IN RETURN HOWS
POLLUIANIH HOI LISTED WERE NOT DC1EC1LD AT ANY SAMPLE POINT
L-IESS TIIANI N-P-NOT DETECTED.
ACID EXTRACT
BASE-NEUTRALS
HE1ALS
INFtUENT
4381*
2*421
103474
4341
22*
242837
213417
90401
30389
20014
7*98
40»»4
3,9
.3
9.8
3.4
3.9
28. 9
3.*
74.8
3.9
.3
47. 3
N-D
1.2
H-D
.7
H-D
.3
N-D
1.3
H-D
.3
.3
N-D
H-0
.2
.2
.2
.3
N-D
N-D
N-D
H-D
10.4
12.9
IOIAL*
OUT
77391
31*931
1*7933
12344
l*.t
944133
224244
242171
20433
241433
1930
22207
• 4
N-D
H-0
1.4
L 0.1
17.3
N-D
1.9
.1
N-D
2.2
.2
A.I
.2
.2
L 0.1
.4
.9
1.3
.2
N-D
.4
.1
.1
.2
.3
.3
.3
.3
4.1
.3
2.2
140
47.4
EFFLUENT
34 7»
4707
14*87
409
9.2
1*1343
184437
171*2
14327
2843
3279
734B
.4
N-D
N-D
3.3
H-P
17.2
N-D
.8
H-D
H-D
i.a
.2
1.4
H-D
.2
N-D
H-D
H-D
.4
H-D
N-D
.4
N-D
N-D
H-D
.2
H-D
H-D
N-D
N-D
H-D
H-D
N-D
2.7
PR 1 HART
SLUDGE
553*
44432
83444
4400
3.8
44331
1*43
24*04
970
24273
43.3
3324
N-D
N-D
H-D
L O.I
L O.I
.1
N-D
.7
.1
N-D
.4
N-D
1.3
.2
N-D
L O.I
.4
.*
.7
.2
N-D
H-D
.1
.1
.2
.1
.3
.3
.3
1.7
.2
,4
38.0
25.3
SECONDARY
BLUDOE
48373
270412
299082
7537
4.1
104237
33424
218073
S79B
2I23I3
412
11313
H-D
N-D
H-D
H-D
H-D
H-
N-
H-
N-
H-
H-
H-
3
H-
H-
N-
H-
N-
H-
H-
u_
H-
H-
H-
H-
N-
2
N-D
H-D
N-D
2.4
.3
1. 8
122
39.4
-------
NABS BALANCE IN POUMUB PER DAY
fUK SAMPLE PATE ENUINO BI0102 AT OBOO HOURS
FRAC IIOH
NCTALS
MON-CONV. METALS
PARAHETER
CYANIDE
LEAP
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
PARIUH
»ORON
CALCIUN .
COBALT
IRON
MAONEBIUH
HANOANE8E
BOBIUH
TITANIUM
INFLUENT
TOTAL*
OUT
4.0
N-P
L O.I
17.1
.3
24,3
17.4
14.2
10B32
1.7
444
2170
74.8
4407*
3.1
17.B
33.•
L 0.
38.r
10.»
1*4
tmuENi
13.7
H-D
M-P
N-P
N-P
7.8
49.1
3.9
14.3
BBOI
2.0
40. «
IB42
43.0,
9*744
N-P
PRIMARY
ILUDOE
1.3
14.2
L O.I
II. t
l.f
ft. t,
NOT RUN
NOI RUN
HOT RUN
NOT RUN
NOI RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
SECONDARY
8LUPOE
2.B
21. «
N-P
27.0
r.o
100
NOT RUN
NOT RUN
HOT RUN
HOI RUN
HOT RUH
HOT RUH
NOT RUN
HOT RUN
NOT RUN
HOT RUN
» TOTAL HASB OUT IS NOT ADJUSTED BY HASS CONTAINEP IN KEIURM FLOU8
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-IESS THAN! M-O-HOT DETECTED.
-------
FRACTION
CONVENT10NALS
NON-CONVENT IONALB
VOLATILEB
NASfi RETURNED TO PLANT IN POUNDS PER DAT
FOR SAHPLE DATE ENDING 810302 AT 0800 HOURS
PARAMETER
BOD
TOTAL SUSP. SOLIDS
COD
OIL I OREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIS8. SOL IPS
TOTAL VOLATILE BOLID9
VOLATILE DISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITKOOEN
TOC
BENZENE
CHLOROBENZENE
J.I.I -TRICHLOROETHANE
CHLOROFORM
1»2-TRAN8-DICHLOROETHYLENE
ETHYLBENZENE
HETHTLENE CHLORIDE
TOLUENE
2r4-MHETHYLPHENOL
PHENOL
I>2i4-TRICIILOROt>EN2£NE
If3~MCHLOROBENZENE
1.4-DICHLOROBENZENE
lt2-DIPHENYLHYDRAZINE
FLUORANTHENE
BI8(2-CNLOROETIIYOXT> METHANE
BISI2-ETHYLHEXrL> PHTHALATE
DI-N-BUTYL PHTHALATC
DI-N-OCTYL PHTHALATE
DICTHYL PHTHALATE
CHRY8ENE
ANTHRACENE
FLUORENE
PHENANTHRENE
PYRENE
ARSENIC
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
Z1HC
FULLUIANT6 N(lf LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
I -LEB3 TMAMI N-D-NOT DETECTED.
ACID EXTRACT
IIASE-NEUTRALS
METALS
DIOESTEff
SUPERNATANT
298
978
914
28.3
.1
189?
1324
3»9
270
329
90.0
32 J
L O.I
L O.I
L O.I
L O.I
L O.I
.3
L 0.1
.1
N-D
L 0.1
L 0.1
I 0.1
L O.I
L 0.1
L O.I
N-D
L 0.1
L O.I
L O.I
L O.I
L O.I
N-0
L O.I
N-D
L O.I
L 0.1
L O.I
.3
,2
L O.I
.1
L 0.1
.1
L O.I
./>
VACUUM FILTER TOTAL NABS
FILTRATE RETURNED
IS. 2 271
VS. 9 474
US 1031
9.7 34.1
L O.I .4
440 2339
343 Ii4»
99.7 497
37.0 307
22.7 3S2
29.0 IIS
90.0 371
L O.I L 0.
N-0 L 0.
N-0 L 0.
N-0 L 0.
N-D L 0.
N-0 .3
L 0.
L 0.
L 0.
L 0.
N-D
L 0.
L 0.
N-0
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
M-0
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
.1
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
I 0.
L 0.
L 0.
L
I
L
L
L .
L
*
.2
L 0.1
.1
L 0.1
.1
L 0.1
.7
-------
MASS KEIIIRNEli TO PLANT IN POUNDS flK PAY
FOR BAMKLt HA It CNMND 010J02 AT 0800 HOURS
f ft AC 11 OH
NON-CONV. HE TALE
PAKAHKIEfi
ALUMINUM
ftARIUH
iOROH
CALCIUM
CObALT
IKON
MAGNESIUM
HAN0ANESE
hOLYbl'ENUM
800IUH
VANADIUH
TTTRIUH
DIUEBIEfc VACUUM FILTER TOTAL MASS
6UFEMATAMT FILTRATE RETURNED
12. S
.1
.2
217
L O.I
9.0
12. S
2.1
L O.I
216
L O.I
1.
L
L
66.
L
1.
14. J
.1 .4
.1 .2
20]
.1 L O.I
10.6
t.7 42.2
.9 2.6
N-D L O.I
63.2 28 I
N-D L 0.1
L 0,1
L 0.1
L O.I
fOlLUlAMIS NOI LISTED UEfiE NOT KETECTEO AT ANY SAMPLE POINT
L-LESS THANI N~D-»NOT OETtCTEP.
-------
MASS BALANCE IN FOUNDS PER I'AY
FOR SAMPLE PATE EMDIHO 610303 AT 0800 HOURS
FRACTION
CONVENT IOMAI.8
MOM-CONVENT IUNAtS
o
u>
VOLATILES
ACID EXTRACT
BASE-NEUTRALS
HE TALE
PARAMETER
BOD
TOTAL SUSP, SOLIDS
COD
OIL I OKEABE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS, SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA HITROOEN
TOC
BENZENE
Ir1tI-TRICHLQROETHAME
lrl»2-TRICHLOROETHANE
CHLOROFORM
ETHYLBENZEHE
HETHYLENE CHLORIDE
TRICIILOHOFLUOROMETMANE
TETRACHLOROETHYLENE
TOLUENE
TRICIUOfiOETHYLEHE
2r4-DICHLDROPHENOL
2»4-DIMETHYLPHENOL
PHENOL
ACENAPHTHENE
lt2t4-TRlCHLOROBENZENE
BIX2-CHLOROETHYL) ETHER
Irl-DlCIILOROBENZCNE
lr4-Dm«.OROBEHZENE
I r2-DIPIIENYLHYDRAZINE
FLUORANTHENE
NAPHTHALENE
•ISI2-ETHYLHEXYL> PHTHALATE
PI-N-DUTYL PHTHALATE
DI-N-OCTYL FHIHALATE
METHYL PHTIIALATC
DIHETHYL PHTHALATE
l*2-BrNZANTHRACENE
CHRYSENE
ANTHRACENE
FLUORENE
PHENANIHRENE
PYRENE
ANTIMONY
ARSENIC
INFLUENT
i3»»4»
47IB3
2S8U9
3910
ISA
401244
332813
»7»78
32877
43101
4843
88447
2.3
1.1
N-D
34.3
3.3
37.3
l.T
10. A
71.3
4.0
.»
N-D
84.0
.4
3.4
1.2
1.4
3.4
.3
.4
N-D
1.4
.4
N-0
.3
N-D
H-D
H-D
N-D
.4
M-D
.4
3.3
H-D
TOTALB
OUT
83431
240487
333788
17432
23,4
33*7*8
299142
202320
30302
17213?
3342
30f4l
.3
L O.I
.4
12.1
.4
23,3
N-D
L 0.1
3,0
.3
N-D
.5
,2
.1
2.0
N-D
N-D
H-D
N-D
.3
1.0
N-D
.8
13.4
I.f
7.7
L O.I
L O.I
.1
L 0.1
.2
.3
2.4
3.9
EFFLUENT
7*42
4844
71383
824
13.*
24*88*
24302S
2*432
24710
4*42
43*3
12*04
.3
N-D
.3
II. 0
.3
23.3
N-D
N-D
2.7
.3
N-P
.3
N-D
N-D
1.1
N-P
N-D
N-0
N-P
N-P
N-D
N-D
,8
13.4
I.V
7.7
N-0
N-D
N-D
H-D
N-0
N-D
N-D
N-D
PRIMARY
8LUDOE
34*8
24*04
448*1
3300
1.8
28803
1*31
17410
934
14777
85.3
1904
N-P
L 0.1
,1
N-P
,1
N-D
N-P
L O.I
.8
.2
N-P
N-D
.2
,1
.*
N-P
N-D
N-D
N-P
.3
1.0
N-D
N-P
N-P
N-D
N-D
L 0.1
L 0.1
.1
L O.I
.2
.3
,2
.4
SECONDARY
SLUDOE
71*71
204*17
21*312
11120
3.*
241104
34IB4
133438
3038
130420
844
14333
N-D
N-P
N-D
1.1
N-D
N-D
H-
N-
H-
N-
H-
H-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
M-
N-
N-
N-D
H-D
N-P
2.2
3.3
* TOTAt HABS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOUB
TUIIUIANrS HOT LiaiED UERE NOT DETECTEB AT ANY SAMPLE POINT
L-IF6S TIIANI N-Ii-NOT DETECTEti.
-------
NABS MLANCE IN POUHIli PER DAY
FOR SAMPLE PATE ENDINO 010301 AI 0100 HOUK8
FRACTION
HETAL8
MON-CONV. It El ALB
PARAMETER
DERVLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAK
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
DARIUM
•ORON
CALCIUM
CO*ALT
IRON
MAGNESIUM
HANOAHEBE
BOD1UH
TITANIUM
YTTRIUM
INFLUENT
1.2
12.4
43.3
24.3
it.S
23.0
.1
17.4
2.2
*4.4
1034
44.7
4».S
14174
2.2
827
27*f
»3.3
»70«S
N-D
3.1
TOTAL*
OUT
.8
10.2
134
St. 3
44.1
44.3
L O.I
48.4
».4
1SI
,.
-
-
-
-
-
.
-
-
~
-
EFFLUENT
N-D
• .0
3.3
4.4
41.7
14.3
N-D
It. 3
.3
14. 4
SS.l
4.4
18.7
12333
2.7
24.4
2471
41. 1
• 7B3*
it.a
N-D
PRIMARY
SLUDGE
.2
.4
24. t
I3.S
.•
S.4
L O.I
4.1
i.r
47. a
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
WOT RUN
SECONDARY
SLUDOE
.4
1.8
122
3f.4
1.4
21.4
N-D
29. f
7.2
lit
NOT SUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
* TOTAL MASS OUT IB NOT ADJUSTED ST MASS CONTAINED IN RETURN FLOHB
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS THAN! M-D-NOI DETECTED.
-------
MASS HALAMCC IN POUNDS PER DAY
FRACTION
CONVENTIONALB
NON-CONVENT10NALB
VOLATILE*
Ln
FOR SAHF'LE PATE ENDING 810304 AT OBOO HOURS
PARAMETER
•OP
TOTAL SUSP. SOLIDS
COD
OIL t OREA8E
TOTAL PHENOLS
TOTAL SOLIDS
10TAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL, SUS, SOLIDS
AHHONIA NITROOEN
TOC
•ENZENC
Irltt-TRICHLOROETHANE
CHLOROFORM
CTHYLBEHZENE
NETHVLENE CHLORIDE
TETRACHLOROETHrLENE
TOLUENE
IRICHLOROEIHVLCNE
2>4-DlHETHYLPHEHOL
PHENOL
ACEMAPIITHENE
lr2>4-TRlCHLOROBENZENE
I,2-PICHLOR08ENZENE
1,3-PICHLOROBENZEME
1>4-D1CHLOROBENZENE
Ir2-DIPHEHYLMYDRAZINE
FLUORANTHENE
NAPHTHALENE
8IB<2-ETHYLHEXVL> PHTHALATE
OI-N-DUIYL PHTHALATE
METHYL PHTHALATE
!>2-B£NZANTHRACENE
CHRYSENE
ANTHRACENE
FLUOftENE
PHEHANTHRENE
lNDENO(l>2i3-CiD) PYRENE
ANTINONY
ARSENIC
DLRYLLIUH
CADMIUM
CHRON1UH
COFFER
CYANI DC
• TOTAL MASS DUI IS NOT ADJUSTED BY HA9E CONTAINED IN RE IURN FLOUS
FUIIUIANIS NOT LISTEd WIRE NOT DETECTED AT ANY SAHPLf POINT
I -I ESS IHANI N-D-NOT I'LItCIEtl.
ACID EXTRACT
»ABE-NEUTRA18
METALS
INFLUENT
133017
II559B
283034
I043I
131
3U23Z
399090
114331
47304
44823
4334
1040*7
3.3
2.2
27.2
7.9
43. A
12.0
53.8
2.3
1.9
47. S
,4
4.1
M-D
l.»
I.T
.3
N-D
N-D
l.»
1.0
.3
N-D
N-D
.3
,4
N-D
N-D
N-D
4.4
3.8
6.3
34. B
24.0
7.0
TOTAL*
OUT
113448
223*02
403*73
1*831
30,0
310307
334884
1824*7
21137
141374
4*24
41824
1,1
.4
14.0
4.0
• .*
4.B
a.i
.7
N-D
3.7
N-D
3.0
,2
.3
,7
N-D
.3
3.4
1,1
.3
.3
.1
L 0.1
L O.I
.3
,2
.2
.2
3.4
.9
3.4
131
33.0
28.3
EFFLUENT
14S80
B«92
472?3
1122
22,4
308424
300019
2130*
I43BO
472*
3*23
22431
I.
.
12.
3.
8.
4.
7.
•
N-D
3,4
N-D
1,1
N-D
.3
.4
N-D
H-D
H-D
I.I
.3
.3
N-D
H-D
N-D
.3
N-D
N-D
N-D
N-D
N-D
3.4
4.2
N-D
23.3
PRIMARY
SLUDGE
10*04
2IB08
323*4
3271
1.3
23*32
2124
14727
43*
14303
31.0
1402
N-D
N-D
L O.I
L O.I
.2
,3
.3
L 0,1
N-D
.3
H-D
,8
.2
H-D
.1
N-D
.3
.4
N-D
N-D
N-D
.1
L O.I
L O.I
N-D
,2
.2
.2
.2
L O.I
.2
14.2
4.2
1.8
SECONDARY
8LUDOE
8»944
1*3402
284284
13438
4.3
22814*
32747
144441
4118
140344
448
179*3
N-D
N-D
1.0
N-D
N-D
H-D
N-D
N-D
N-D
N-D
N-D
3,1
N-D
N-D
N-D
N-D
N-D
2.B
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
3.2
.3
1. 8
133
44.8
1.2
-------
MASS BALANCE IN POUNDS PER DAT
FUR SAMPLE PATE ENP1NO BI0104 AT 0800 HOURS
FRACTION
nciAis
MON-COMV. METAL*
PARAMETER
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
PAR IUN
»ORON
CALCIUM
COBALT
IRON
HAOHESIUM
NANOANESE
HOLYPDENUH
SODIUM
TITANIUM
VANADIUM
YTTRIUM
INFLUENT
TOTAL*
OUT
31.2
L 0,1
33.8
2,2
12?
3120
37,0
44.3
I99I»
2.»
B»0
3U7
»l.B
i.O
1IOB47
H-D
3.B
72.B
28. S
L 0.1
95.3
II.B
Uf
EFFLUENT
N-D
N-D
29.2
.1
17.7
PRIMARY
BLUDOE
4.0
L O.I
1.1
.7
21.2
BECONPARY
SLUD0E
24.9
N-D
27.0
10. B
130
141
4.2
27.2
12117
N-D
BV.7
2923
9B.V
H-D
9140*
19.7
N-P
H-0
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
« TOTAL MASS OUT IS NOT ADJUSTED »Y MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L-LE6S THANI H-D--MOT PETECTEP.
-------
MASS BALANCE IN POUNDS UK Ml
FRACTION
CONVENTIONAL8
PARAMETER
too
TOTAL SUSP.
COD
OIL I (INCASE
FOR SAMPLE DATE ENDINO BI0309 AT 0000 HOURS
SOLIDS
NON-COHVENTIOHALS
7
o-<
VOLAIILCB
ACID CXTR/tCT
VASE-NEUTRALS
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL 0188, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE PISS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHHOHIA NITROOEN
TOC
IENZCNE
111 • I-TRICIILOROETHANE
CHLOROFORM
ETHYLBENZCNE
HETIIYLENE CHLORIDE
TETRACNLOROETHTLENE
TOLUENE
TRICHLOROETIirLENE
PHENOL
1,2.4-TRICHLOROPENZENE
Itl-DICHLOROBENZENE
FLUORANTHENE
NAPHTHALENE
BI8<2-ETHYLHEXYL> PHTHALATE
BUTYL BENZYL PHTHALATE
DI-N-OCTYL PHTHALATE
DIETHYL PHTHALATE
lr2-BENZANTHRACEHE
1I,12-BENZQFLUORANTHENC
CHftYSENE
ANTHRACENE
FLUORENE
PHCNANTHREHE
PYREHE
ANTIMONY
ARSENIC
BERYLLIUM
CADHIUH
CHRONIUN
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
< IOIAL MASS OUT IS HOI ADJUSTED BY NA3S CONTAINED IN RETURN FLOU8
FOILUTAIITB NOT LISTED HIKE NOT DETECTED AT ANY SAMPLE POINT
I-I£38 TMANI M-D-HOI l-EUCTEf.
HETAL8
INFLUENT
HOT RUN
MOT HUH
NOT RUN
NOT RUN
HOT RUN
NOT RUH
HOT RUN
HOT RUH
HOT RUH
NOT RUH
NOT RUN
HOT RUN
NOT RUH
NOT RUH
NOT RUN
MOT RUH
NOT RUH
NOT RUN
MOT RUH
NOT RUH
HOT RUH
HOT RUN
NOT RUN
MOT RUN
HOT RUN
HOT RUH
HOT RUH
NOT RUH
MOT RUH
HOT RUN
NOT RUH
HOT RUH
NOT RUH
HOT RUN
HOT RUN
NOT RUH
HOT RUH
MOT RUH
MOT RUN
MOT RUH
MOT RUN
NOT RUN
NOT RUM
MOT RUH
NOT RUN
HOT RUM
TOTAL*
OUT
197880
320842
434**4
834*7
40.0
734fU
4UOS7
259030
3HI4
204582
4I7B
313*4
1.7
2.1
I8.B
7.7
123
4.9
24.3
7.2
220
4.2
.4
2.9
3.4
1.3
.2
.4
4.8
L 0.
L 0.
L 0.
L 0.
L 0.
.2
2.2
L O.I
1.0
1.4
7.1
• »»
43.9
34.5
42.4
.4
S8.2
CFFLUEHT
2243*
14831
f7442
288 IS
40.9
3fS7«4
383*19
333*2
44*17
8479
33*0
31781
1.7
2,1
17.8
7.4
123
4.7
22.0
7.2
220
.4
.4
N-D
N-D
1.3
N'D
.4
A. 8
M-D
N-B
M-D
M-D
N-D
N-D
M-D
M-D
N-D
M-D
3.8
11.4
N-D
28.4
N-D
N-D
23.3
PR1HARV
SLUDOE
2274
24423
33734
3073
.*
27414
1224
142*4
37*
1 3841
32.9
7*1
H-D
N-D
L 0.1
L 0.1
H-D
.2
.3
L O.I
N-D
,t
H-P
,2
.4
N-D
.2
H-D
N-D
L 0 I
L 0 1
L 0 I
L 0 1
L 0 1
.2
.2
L 0.1
.3
L 0.1
L 0.1
4.0
2.7
1.2
2.B
L O.I
1.4
SECOHDARY
SLUDOE
133147
27*408
3037VS
23407
4.8
3I03S4
30*48
1*0344
4118
104244
734
1*7*2
M-D
N-D
.*
H-D
M-D
M-D
2.0
N-D
N-D
3.2
H-D
2.3
3.0
N-D
N-D
M-D
H-D
H-D
N-D
H-D
N-D
N-D
H-D
2.0
M-D
.7
1.4
3.2
184
41.2
4.V
3*. 4
.3
33.3
-------
MASS BALANCE IN POUNPB PER DAY
FOK SAMPLE DATE CNPIMO 810309 AT 0100 HOURS
Ft) ACT I ON
METALS
NUN-CONU. HE IALB
PARAMETER
SILVER
ZINC
ALUHINUH
•ARIUN
IORON
CALCIUM
COSALT
IRON
MAGNESIUM
MANOANESE
SOPIUM
INFLUENT
TOTAL*
OUT
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NO I RUN
NOT RUN
NOT RUN
NOT RUN
NOI KUN
NOT RUN
HOT RUN
14.8
218
EFFLUENT
.4
17.1
291
9,7
23. •
U32«
3.4
144
JJfO
74. J
1135*4
PRIMARY
BLUDOE
.4
10.4
HOI RUN
N0I RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
ILUPOE
14.0
JV1
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
00
« TOTAL NASB OUT IB NOT ACJU8IEH *T MASS CONTAINED IN RETURN FLOU8
POLLUTANTS MOT LISTED WERE NOT ['EJECTED AT ANY SAMPLE POINT
L-IESS THAHI N-D-NOT HETECIED.
-------
HABS ttALANCE IN POUNDS PER DAT
FRACTION
CONVENTIONAL8
NON-CONVENTIONALB
PARAMETER
BOD
TOTAL SUSP
COD
OIL I GREASE
FOR SAMPLE DATE ENDINO 810104 AT 0800 HOURS
SOLIDS
VOLAIUEB
VO
ACID EXTRACT
BASE-NEUTRALS
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL OIBS, SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOTAL VOL. BUS. SOLIDS
AHHONIA NITROOEN
TOC
BENZENE
CHLOROBENZCNE
1,1.1-TRICHLOKOEtHANE
1 • I•2-TRICHLOROE THANE
CHLOROFORH
ETMYLBENZENE
HETHYLEME CHLORIDE
TETRACHLOROETHTLENE
TOLUENE
TftlCHLOROETHYLENE
2.4-DICHLOROPHENOL
PHENOL
1,2,4-TR1CHLOROSENZEHE
li3-DICKLORO»ENZENE
lr4-DICIILOftOȣHZENE
I>2-DIPHENVLHYDRAZINE
FLUOftANTHEHE
NAPHTHALENE
BIBI2-ETHYLHEXYL) PHTHALATE
DI-N-BUTYL PHTHALATE
DIETHYL PHTHALATE
ANTHRACENE
FLUORENE
PHENANTItRENE
PYRENE
ANTIHONT
ARSENIC
BERYLLIUH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
HERCURV
« TOTAL HASS OUT IB NOT ADJUSTED BY NABS CONTAINED IN RETURN FLOUB
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L'LESS THANI N-P-NOr DETECTED,
NETAtS
INFLUENT
172780
144231
344431
4743
241
983744
438271
23914*
12473*
(10411
9097
13B03I
I8,t
1.3
4.4
N-D
,41.3
7,4
l».8
13.*
904
2.9
».3
211
2.9
.8
2.1
.4
N-D
N-B
1.3
.8
,8
.4
.4
,4
N-D
N-D
4.2
N-D
3.1
143
3B.3
23.7
N-D
.2
TOTAL*
OUT
170100
334434
939113
2*17*
fO.l
728239
373422
32*719
72844
234808
3230
47724
8,1
N-D
1.2
.1
17.9
2,0
f.4
3,3
319
.7
4.9
18.1
4.8
.8
1.2
H-D
2.9
3.8
N-D
12.2
1.*
N-D
N-D
.2
2.1
3.4
7.2
1.1
3.2
182
41.4
21.*
43.*
.4
EFFLUENT
22474
14143
80713
1*22
78.8
340317
344374
787*1
44874
11*19
24*0
28097
4,*
H-0
1.2
H-0
14.1
1.*
f.4
1.*
298
.4
4.9
IB.I
1.9
.8
1,2
N-B
N-B
N-D
N-D
N-D
1.*
N-K
N-D
N-D
N-D
H-D
N-D
N-D
1.*
20,0
N-0
13.1
N-D
N-D
PRIMARY
SLUDOE
3482
3*0*3
39340
2247
.*
40*V2
IB**
24219
370
23382
34.4
1314
L 0.1
N-D
N-D
.1
.1
.1
N-D
N-D
2,9
.3
N-D
N-D
.4
H-D
N-D
N-B
.3
.4
N-
N-
N-
N-
H-
,2
.2
,3
,4
L 0.1
.4
22,2
11.2
1.4
10.1
,1
SECONDARY
SLUDOE
143*42
2f*400
3*3042
23010
10.4
32474*
2734*
22470*
33*8
221311
904
18333
I.I
N-D
H-D
N-D
1.3
N-D
H-D
1.4
94.0
N-D
N-D
N-D
2.7
N-0
N-D
N-D
2.2
3.2
N-D
12.2
N-D
N-D
N-D
N-D
1.*
3.1
4.B
1.0
2.*
140
30.4
7.4
33.8
.3
-------
MASS BALANCE IN POUND* PCM PAY
FOR SAMPLE PAIE ENPINO 010304 At 0100 HOURS
FRACTION
METALS
NON-CONV, HETAtB
O
I
PARAMETER
NICKEL
SILVER
ZINC
ALUHIMUH
BARIUH
BORON
CALCIUH
CORAL I
IRON
NAONEIIUN
HANOANCBE
HOLVBDENUn
SODIUM
TITANIUM
VANADIUN
YTTRIUM
INFLUENT
TOTAL*
OUT
EFFLUENT
PRIHADV
•LUPOE
SECONDARY
•LUDOE
22.•
2.5
110
2893
94.•
44.4
23178
21.1
1201
17*3
114
S.I
11904*
N-C
2.9
3.8
34.1
10.0
224
N-D
.4
13.0
IT*
• ••
24.9
17480
4.»
74.•
1079
49.3
H-ft
f4t49
24.9
N-B
N-D
10
1
42
NOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
MOT RUM
HOT RUN
HOT RUN
HOT RUN
HOT RUN
29.2
• .3
144
NOT RUN
NOT RUN
HOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUN
HOT RUH
HOT RUH
HOT RUN
HOT RUH
NOT RUN
« TOTAL MASS OUT IB NOT APJUBTED BY MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED MERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS THAN* H-D'MOI DETECTEU.
-------
FRACTION
CONVENT(ONALS
NDN-CONVENIIONALB
VULAT1LEE
NAS8 BALANCE IN POUNDS PER DAY
FOR SAHFLE DATE ENDINO 810307 AT 0800 HOURS
PARAHETER
DOD
TOTAL SUSP. SOLIDS
COI)
OIL 1 OREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL PISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIS9. SOLIDS
TOIAL VOL. SUB. SOLIDS
AHHOHIA NITROGEN
IOC
DENZENE
CHLOROSENZENE
1.2-DICIILOROETMANE
1•I>1-TRICHLOROETHANE
1,1-DICHLOROETHANE
I•1f2-TRICHLOROETHANE
CHI.OROFORN
I.I-D1CHLOROETHYLENE
1,2-rRANS-nlCHLOROETHYLEME
ETHYLDEHZENE
NETHYLENE CHLORIDE
TRICHLOROFLUORONEIHANE
TETMCHL080ETHYLENE
TOLUENE
TRICHLOROETHYLENE
VINYL CHLORIDE
2r4t4-TRICHLOROfHEHOL
PARACHLOROMETA CREBOL
2-CHLOROPHENOL
2i4-DICHLOROPHENOL
2>4-DIHETHYLPHENOL
4-NITROPHENOL
PEHTACHLOROPHENOL
PHENOL
ACENAPHTHENE
lf2.4-TRlCHLORODENZENE
I»2-DICHLORO»EHZENE
1>3-DICHLURO»ENZENE
1.4-DICHLQROBENZENE
FLUORANTIIENE
NAPHTHALENE
DISI2-ETHYLHEXYL) FHTHALATE
ANTHRACENE
FLUORENE
FHENANTHKENE
* fOTAL HASS OUT IS HOT ADJUSTED BY HASB CONTAINED IN RETURN FLOUB
FOLLIITAHTS NUT LISTED MERE NOT DETECTED AT ANY SAHPLE POINT
L-LEES THANI N-D-NOT I'ETECTED.
ACID EXTRACT
BASE-NEUTRALS
INFLUENT
102*3*
144048
2BB2B3
16B17
at?
311342
34442B
20282*
»334»
10*480
6178
12)331
11.7
N-0
3.8
30.1
N-0
N-D
38.8
J.B
1.4
17.2
3S.7
1.0
4.9
123
N-0
227
.3
.7
N-D
1.4
N-0
12.4
3.1
38.3
N-D
1.7
N-D
.7
N-D
H-D
f.J
1.7
N-D
N-D
N-D
TOIAL*
OUT
83387
31310*
734831
32074
143
703430
340121
324778
31071
273703
3490
34138
4.3
1.4
.2
23.7
.3
.4
20.3
1.0
N-D
14. 8
33.4
l.f
B.»
70.3
4.8
N-D
N-D
1.0
.3
H-D
1.4
7.0
N-D
2.3
.2
8.1
.2
1.0
.1
4.2
8.7
1.7
.1
.2
.3
EFFLUENT
21420
13747
7»»24
1*18
128
3240ft
312032
5342*
44Ilf
MSOf
2877
31*71
4.2
1.4
N-D
20.8
N-D
N-D
IB.*
1.0
N-D
7.0
2V.1
1.*
7.4
34.3
2.2
N-0
H-0
1.0
.3
N-D
1.4
7.0
N-D
2.2
N-D
1.0
N-D
1.0
N-D
N-D
N-0
N-D
N-D
N-D
N-D
PRIHARV
ILUtiOC
4390
33*27
7*133
232
I.B
37827
1820
21208
473
20733
33.2
2214
.1
N-0
.2
.4
.3
.«
.2
N-D
N-D
,2
.2
N-D
N-D
4.1
1.3
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
.3
.2
1.7
.2
N-D
.1
.7
1.*
1.7
.1
.2
.3
SECONDARY
8LUDOE
37377
313433
373770
2**04
14.*
33*704
2424*
247*41
4477
241443
340
21*31
N-D
N-0
N-D
2.9
N-D
N-D
1.4
N-D
N-D
7.4
24.1
N-D
1.3
II.*
1.3
N-D
N-D
N-D
H-D
N-D
N-D
N-D
N-0
N-D
N-D
9.4
N-D
H-D
N-D
3.9
4.8
N-D
N-D
, N-D
N-D
-------
HABS MLANCE IN POUNDS tfft DAY
FOR SAMPLE OATE ENDING 810107 AT 0800 HOUK8
FRACTION
HETAL6
NON-CONV. METALS
10
PARAMETER
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
HICKEt
SILVER
ZINC
ALUMINUM
•ARIUH
IORON
CALCIUM
COtALT
IRON
nAONESIUH
MANOANEBE
HOLVDDENUN
SODIUM
TITANIUM
VANADIUM
INFLUENT
a. s
1.4
l.ft
N-P
48.0
17.8
12.7
N-P
N-D
18.3
2.4
82.4
2092
41.2
48,0
IBIBV
B.»
122V
108?
101
N-D
83434
17.2
2.4
TOTAL*
OUT
.3
1.8
1.0
4.3
230
71.7
24.2
44.1
L O.I
12.2
».»
241
_
_
-
-
_
»
-
_
-
-
_
-
EFFLUENT
N-P
N-D
M-P
N-P
11.8
M-D
18.9
N-D
M-P
M-P
.1
«4.4
144
a. A
27.8
13024
4.7
113
2338
47.1
1.3
81849
21.7
N-D
PRIMARY
SLUDOE
.1
.7
L O.I
.3
21.7
14,1
1.5
10. 1
L 0,1
4.1
1.1
44.1
NOT RUM
HOT RUM
NOT RUN
HOT RUN
NOT RUN
NOT RUN
HOT RUM
HOT RUN
HOT RUN
HOT RUM
NOT RUN
HOT RUM
SECONDARY
SLUDOE
N-P
I.I
.»
4.0
If4
37.4
4.2
14.0
N-D
28.1
8.1
180
HOT RUM
HOT RUH
HOT RUH
HOT RUH
NOT RUH
HOT RUH
HOT RUH
HOT RUM
HOt RUH
HOT RUH
HOT RUH
HOT RUM
* TOTAL MASS OUT IS NOT ADJUSTED bl HABS COHTAINED IN RETURN FLOUB
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT '
L-LESS THAN I N-O'NOT DETECTED.
-------
FRACTION
CONVENTIONALS
NON-CONVENTIOHALS
VOLATILEB
MASS VALANCE IN POUNDS PER DAY
FOR BAHPLE HATE ENDING BI030B AT OBOO HOURS
PARAMETER
DOD
TOTAL BUSP. SOLIDS
COD
OIL t OREABE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIS9. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIBS. SOLIDS
TOTAL VOL. SUB. 801IPS
AMMONIA NITROGEN
TOC
BEHZEHE
IiI»I-TRICHLOROETHAHE
1>Ir2-TRICHLOKOETHAHC
l>l>2t2-TETRACHLOROETHAHE
CIILOROFORH
1*2-TRAH8-DICHLOROETHYLCNE
ETHYLBCHZEHE
HETHYLEHE CHLORIDE
TR1CHLOROFLUOROHEIHAHE
TCIRACHLOROETHYLEHE
TOLUENE
TftlCHLOROETHYLENE
2>4f4-TRICHLOROPHENOL
PARACHLOROHETA CREBOL
2.4-DICHLOROPMENOL
4-NITROPHEHOL
PENTACHLOROPHEHOL
PHENOL
li2>4-TKICHLORODEHZEHE
1.3-PICIILOROPEMZEME
1.4-DICHLORODEHZENE
FLUORANTH£HE
HAPHTHALENE
»IS(2-ETHYLIIEXYL> PHTHALATE
ANTHRACENE
PIIEHAHTHREHE
PYREHE
ANTINOMY
ARSENIC
BCRYLLIUH
CADHIUH
CHROHIUH
COPPER
CYANIDE
« TOIAL MflBB OUT IS N01 APJUSTEP BY MASS CONTAINED IN RETURN FLOWS
fOLlUIANFS NOT LISTED UERE NOT DETECTED AT ANY SAMPLE POINT
I-ItSB TIIANI H-D-HOT (lETtCTED.
ACID EXTRACT
BASE-NEUTRALS
METALS
INFLUENT
I2231B
92291
201824
7443
244
293B4B
24IS77
124*09
88480
3B224
All*
13I4V2
4.*
N-0
N-D
N-D
1B.O
.4
3.2
21.7
.9
B.O
79.2
4.3
.3
.3
2.1
H-D
N-D
38.7
2.1
H~D
N-0
H-D
4.0
i.e
.3
.3
N-D
N-D
N-D
N-D
N-D
•93
13.4
14.1
TOTAL*
OUT
215874
36927*
3*2350
10B370
42.2
421477
234401
3IB734
43V34
274B40
2431
40933
1.4
,f
.2
.8
12.7
N-D
3.2
40,9
.9
1.3
19.0
1.9
N-D
N-D
1.9
8.3
.9
17.3
4.B
.3
.3
,2
7.8
N-D
N-D
.1
.1
.2
1.3
.7
3.9
397
73.2
13.1
EFFLUENT
1499*
•343
44394
93B
31. V
234974
228233
44478
37142
7S34
2133
22070
1.4
.»
N-D
.8
12.4
N-D
3.0
30.1
.3
1.1
19.1
t.l
N-D
H-D
1.*
• .3
.9
14.7
I.I
.3
.3
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
114
3.3
9.4
PRIMARY
BLUOOE
18992
384*0
40143
1193
2.2
40399
IB99
24119
494
23481
43.9
1230
L 0.1
L 0.1
.2
N-D
.1
N-D
.2
N-D
N-D
N-D
.7
.4
N-D
H-D
N-D
N-D
N-D
.4
.9
N-D
N-D
.2
.4
N-D
N-0
.1
.1
,2
.3
.3
.3
49.1
13.7
.2
SCCONDARY
BLUDOE
179928
310473
447BI3
I04B77
B.I
344742
24249
247941
4118
241823
432
17433
H-
N-
H-
H-
N-
N-
H-
10
H-
N-
N-
N-
N-
N-
N-
N-
N-
N-
B
3.2
H-D
N-9
H-D
7.2
N-D
H-0
H-D
H-D
H-D
1.0
.4
3.2
432
34.0
3.3
-------
HABS BALANCE IH POUNDS PER VAT
FOR SAMPLE tiAtE EN0INO 8I030B AT 0800 HOURS
FRACTION
MEIALS
NON-CUNW. METAL8
PARAMETER
LEAB
DERCUHT
NICKEL
SILVER
ZINC
ALUMINUM
•ARIUN
BORON
CALCIUM
COBALI
IKON
HAONEBIUN
NANOANEBC
SODIUN
TITANIUM
INFLUENT
TOTAL*
OUT
N-B
L 0.1
17.4
.4
44.2
1321
2B.4
10.«
IS3t«
3.1
1*4
2732
as.*
91*03
20.3
41.3
L 0.1
30.0
8.4
20»
EFFLUENT
N-D
N-D
N-D
N-B
13. 9
»A.r
7.0
It. A
I3IB8
3.2
83.4
2422
S». 2
«028B
21.8
PRIHART
BLUOOE
7.3
L 0.1
4.1
1.0
3B.O
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
HOT RUN
BECONPART
BLUDOC
14.0
N-B
23. t
7.*
198
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
* I01AL HABS OUT IS NOT ADJUSTER BY HASS CONTAINED IN RETURN FLOUB
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANT SAMPLE POINT
L-IES8 THAN! N-D'NOT UETECIEII.
-------
HASS BALANCE IN FOUNDS ft ft PAT
FRACTION
CONVENUONALS
PARAMETER
BOD
TOTAL SUSP
COD
OIL I GREASE
FOR SAMPLE PATE END1NB 81030V AT 0000 HOURS
SOL IOB
NON-CONVENTIONALB
VOLATILES
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DI8B. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI88. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA HITROOEN
TOC
BENZENE
If lil-TRICHLOROETHANE
I.I* 2-TRICHLOROETHAHE
CHLOROFORM
1,2-TRANB-DICHLOROETHYLENE
ETHVLBENZEHE
HETHYLEKE CHLORIDE
TRICHLOROFLUOROHE THANE
TETRACHLOROETMYLENE
TOLUENE
TRICHLOROETHYLENE
2-CHLODOPHENOL
2.4-DICHLOROPHENOL
PHEHOL
ACCNAPHTHENE
l»2r4-TRICHLOROBENZENE
li2-DICHLOROBEHZENE
1.3-DICHLOROIENZENE
Ii4-DICHLOR08£NZENE
FLUORAHTHENE
NAPHTHALENE
BIB(2-ETHYLHEXrL) PHTHALATE
DI-N-tUIYL PHTHALATE
ItlETHYL PHTHALATE
CHRY6ENE
ACENAPHTHYLENE
ANTHRACENE
FLUORENE
FHENANTHRENE
PYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
» TOTAL MASS OUT IB NOT ADJUSTED BY HASS CONTAINED IN RETURN FLOWS
POLLUIftHTS NOT LISTED WERE NOT DETECTED AT ANT SAMPLE POINT
L'LESS iHftf'l H-D-NOT DETECTED.
ACID EXTRACT
BASE-NEUTRALS
METALS
INFLUENT
44017
39933
72033
4070
248
1*8418
143103
91874
25093
24843
9424
3834?
4,4
1.9
N-0
4.1
.9
3.4
19.3
1.3
2.3
137
2.3
.3
7.7
47.3
M-D
1.0
N-D
.3
N-D
.9
4.3
2.0
2.3
1.3
N-D
1.9
.3
N-D
.3
,3
N-D
N-B
tt-D
N-B
TOTAL*
OUT
133189
340992
3703413
24177
11.3
37*841
I9S933
1*0*19
20917
1477*7
2420
23494
.7
.2
L 0.1
2.4
N-D
.1
8.1
.4
N-D
3.1
.2
N-D
1.3
.8
.1
1.7
.2
N-D
.2
.9
.7
N-D
N-D
.7
.1
N-D
.1
.1
.3
.4
.3
2.0
l.t
3.4
EFFLUENT
4408
4388
2413S
1934
4.1
14130!
134713
IBB47
19197
3911
1779
9*24
.7
.2
N-D
2.4
M-D
N-D
8.1
.4
N-D
2.4
N-D
N-D
1.3
.2
N-D
,7
N-D
N-D
N-D
H-D
N-D
N-0
N-0
.7
N-D
N-D
N-D
N-D
N-0
N-0
N-D
N-0
N-D
H-D
PRIMARY
SLUDOE
8230
21090
80718
9080
2.9
22474
MSB
12430
922
I2IOB
47.1
2098
N-D
N-D
L 0.1
N-D
N-D
.1
L 0.1
N-D
N'D
.9
.2
N-D
N-D
.4
.1
1.2
42
N-D
.2
.9
.7
N-D
N-D
N-D
.1
N-D
.1
.1
.3
.4
.3
.4
.2
.4
SECONDARY
SLUDOE
122391
219994
3976940
17941
2.7
234044
20192
197414
9038
194378
374
19474
N-D
N-D
N-
H-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
H-
H-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-
N-D
1.4
.7
1.2
-------
MASS kALANCE IN POUNDS PER PAY
FOR SAMPLE DAIE CNDINO BlOJOf At ODOO HOUKB
FRACTION
HETALK
NON-CONV. METALS
PARAMETER
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUHIMUH
•AMIUN
•OROM
CALCIUM
CDHALT
IRON
HAONEBtUH
NANOANESE
SODIUM
TITANIUM
INFLUENT
TOTAL I
OUT
EFFLUENT
PRIMARY
BLUDOE
SECONDARY
ILUDOC
B.2
10.0
N-D
N-D
N-P
N-D
.9
29.4
7*3
10.4
18.4
12527
2.8
312
I7t0
• 1.8
397*1
14.1
9(0
44.2
17.8
41.1
L O.
11.4
4.4
If 2
24.1
N-D
8.8
N-D
N-P
N-D
H-D
7.7
S2.7
9.1
7.7
10912
1.8
«.B
1799
S2.7
1I70V
12.1
92.2
17.4
2.9
10.4
L 0.1
4.4
1.0
47.9
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
904
4*.8
4.9
10.t
N-D
27.0
9.4
117
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
» TOTAL MASS OUT IS NOT ADJUSTED »Y MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-LESB THAN I N-p-MOT DETECTED.
-------
FRACtlON
CONVENT IONAI.S
NON-COHVENTIONALS
VOLATILEB
HASS RETURNED TO PLANT IN POUNDS PER DAT
FOR SAMPLE HATE ENDIND B10J09 AT ONOO HOURS
PARAMETER
HOD
TOTAL SUSP. SOLIDS
COD
OIL I GREASE
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL HISS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DI8S. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROOEN
TOC
BENZENE
CMLORODENZEHE
Ii1tI-TRICHLOROETMANE
Itl-OICHLOROETHANE
1»2-TRANS-D1CHLOROETHTLENE
ETHYL BENZENE
HETHYLEHE CHLORIDE
TRICHLOROFLUOROMETHANE
TOLUENE
PHENOL
1»2r4-TRICMLOROBENZENC
1,J-DICHLOfiOBENZEHE
114-DICHLOROBEHZENE
FLUORANTHENE
NAPHTHALENE
N-HITR080DIPNENTLANINE
BISI2-ETHYLHEXrL> PHTHALATE
DI*N-BUTYL PHTHALATE
DI-N-OCTTL PHTHALATE
DIETHYL PHTHALATE
lf2-BEHZANTHRACENE
ANTHRACENE
FLUORENE
PHENANTHRENE
ANTIMONY
ARSENIC
DERYLLIUH
CADMIUM
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
rOlLUTANTS NOT 11BTED WERE NOT DETECTED AT ANY SAMPLE POINT
L-LESS THAN! N-D*NOT DETECTED.
ACID EXTRACT
BASE-NEUTKAL8
METALS
UIGES1
SUPER*
332
1230
1283
?4.3
,1
2041
811
»74
2AI
711
93, «
4*»
t 0.
L 0.
L 0.
L 0.
L 0.
.1
L 0.
C 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
N-D
L 0.
1. 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
.4
,4
L 0.
.3
L 0.
.2
I 0.
ER VACUUM FILTER
ATAMT FILTRATE
11.0
?A,3
38.3
3.3
L 0.1
3S2
233
3f ,1
22.3
17.9
14.2
20.0
L O.I
N-D
L O.I
N-D
N-D
L O.I
L O.I
L O.I
L O.I
K-0
K-B
I O.I
K-D
N-D
N-D
N-D
L O.I
N-D
L 0.1
L O.I
H-0
L O.I
N-D
L O.I
N-D
L O.I
N-0
N-D
L O.I
L O.I
1 N-D
N-D
t N-D
N-D
1 L O.I
TOTAL MASS
RETURNED
343
1327
1321
»7.e
.a
23V2
1049
1014
283
72»
47. B
48V
L 0.
L 0.
L 0.
L 0.
L 0.
.1
L 0.
L 0.
.1
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.
L 0.1
L 0.1
L 0.1
L 0.1
.4
.4
L 0. 1
.3
L 0.1
.2
L 0.1
-------
HA88 RETURNED TO PLAN! IH POUNDS PER HAY
FOR SAMPLE PATE ENOINO B»OJO» AT OBOO HOURS
FRACTION
METALS
ItOM-CONV. METALS
PARAMETER
ZINC
ALUHIHUH
BARIUM
BORON
CALCIUM
COHALT
IRON
MAONEBIUH
HAHOANESE
MOLYBDENUM
80PIUH
VANADIUM
YTTRIUH
PIOEBTER VACUUM FILTER TOTAL MA8B
SUPERNATANT FILTRATE RETURNED
1.4
13.!
..
208
L
U.
26.
2,
L
13V
L
t
1 L <
r .
' L
L
91.
.1 L
•
7.
•
.1 N-I>
4*.
.1 N-D
L (
>.l 1.4
14.1
.1 .7
.1 .2
29*
.1 L 0.1
17.2
31.2
2.1
L 0.1
t 209
L O.t
>.l .1
-J
00
POLLUTANTS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L»LESS THANI N~D»NOT DETECTED.
-------
MASS BALANCE IM POUNDS PER DAY
FRACTION
CONVENT IONALB
NON-CONVENT InHALB
PARAMETER
ROD
TOTAL SUSP
COD
OIL I ORCASE
POR SAMPLE DATE ENDINO 810310 AT OBOO HOUR6
•OLIOS
-J
VO
TOTAL PHENOLS
TOTAL SOLIDS
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DIfiB. SOLIDS
TOTAL VOL. BUS. SOLIDS
AMMONIA NITROGEN
TOC
VOLATILES BENZENE
Itltl-TRICMLOROETHAHE
Irl-DICHLOROETHANE
l,li2-TRICHLOROETHANE
CHLOROFORM
1.2-TRAH8-DICHLORdEtMYLENE
ETHYLKNZENE
HETHTLCNE CHLORIDE
TRICHLOROFLUOROHETHANE
TCTRACHLOROETHYLEHE
TOLUENE
TRICHLOROETMYLENE
2.4-MCHLOROFHEHOL
PHENOL
1,2,4-TftlCHLOROBEHZENE
112-DICHLDROBENZEHE
Ill-DlCHLOROBENZCNE
It4-DICHLOROBENZENE
FLUDRANTIIENE
NAPHTHALENE
ANTHRACENE
FLUDRENE
PMEHANTHRENE
METALS ANT1HONY
ARSENIC
BERYLLIUM
CADHIUH
CHROMIUM
COPPER
CYANIDE
LEAD
MERCURY
NICKEL
SILVER
* IIHAL MASS OUT 16 NOI APJUB1E1' »Y MflBB CONTAINED IN RETURN FLOWS
POLLUIANIS NOT LISTED UEKE NO! DETECTED AT ANY BAMfLE POINT
L'LESS TtlANI N-D-NOT DE1ECTED.
ACID EXTRACT
BASE-NEUTRALS
INFLUENT
148147
106060
349197
7107
411
444442
336699
121348
32329
69033
9724
101010
4.4
2.4
2.4
N-0
41. a
.7
24.?
20.3
,7
7.7
94.1
2.4
2.7
91.6
2.4
N-D
,3
1.7
H-D
13.1
N-D
N-D
N-D
N-D
4,7
N-D
1.7
64.0
33.0
94.2
H-D
.2
17.8
3.0
TOTAL*
OUT
130382
279339
430639
19818
27.2
937944
29B609
217311
16004
201307
4073
39247
.9
.6
N-D
L 0.1
16.0
N-D
2.3
8.1
.3
.6
11.3
.5
2.4
4.9
36.3
.1
H-D
.9
.6
3.8
.1
.1
.3
.1
1.6
1.1
3.3
341
64.8
43.7
42.4
L 0.1
30.1
7.7
EFFLUENT
10313
7209
42033
3304
21.9
24330S
236099
14321
12019
4306
3603
18123
.9
.6
N-D
H-D
13,0
H-D
2.4
8.1
.3
.6
10.3
.3
2.4
4,3
.9
H-D
N-B
.3
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
H-D
14.4
3.6
33.3
H-D
H-D
H-D
.3
PRIMARY
6LUDBE
11912
7992
48730
1071
1.2
9270
1278
3388
390
3198
33.7
324*
L O.I
N-0
N-B
L O.I
.1
N-D
L 0.1
N-D
H-D
H-D
.8
.2
H-D
.4
•
.
H-D
4
.
1 .
.
,
.3
,1
,2
L 0,1
,3
22.7
10.8
1.7
6.4
L 0.1
3.1
,9
SECONDARY
8LUDOE
107937
264134
339836
11443
4.1
283366
21232
193402
3399
191803
432
13673
H-D
H-D
H-P
H-D
.9
H-
H-
H-
H-
H-
H-
N-D
H-D
H-D
34.3
N-P
N-D
N-D
N-D
2.7
N-D
N-D
H-D
H-D
1.4
1.0
3.2
304
30.4
8.7
36.0
H-D
27.0
6.5
-------
MASS BALANCE IN POUNDS »>£» KAY
FDR SAMPLE HATE ENDING BIOIIO AT oaoo HOURS
TRACTION
METALS
NON-CONV. METALS
PARAHETER
ZINC
ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IKON
MAGNESIUM
HANOANE8E
BODIUM
VANADIUM
INFLUENT
171
304?
30. S
40.4
I 7508
7.4
ISA?
26»4
143
V3244
3.0
TOTAL*
OUT
208
EFFLUENT
27. »
B,
29.
ISO V
2.
4B.
2403
7B.I
PRIMARY
ILUDOE
SECONDARY
ILUDOE
N-D
33.7
NOT HUN
NOT RUM
HOT RUN
NOT RUN
NOT RUN
HOT RUN
HOT RUN
HOT HUH
NOT RUN
NOT RUN
144
NOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOT RUN
NOT RUN
NOT RUN
O
I
CO
o
* IU1AL MASS OUT IS NOT ADJUSTED BT MftSB CONTAINED IN RETURN PLOWS
rOLlUTANTS NOT LISTbd HERE NOT DETECTED A1 ANY SAMPLE POINT
L--LESS THAN! N-D'NOI DETECTED.
-------
MASS BALANCE IN POUNDS PER DAT
FOR SAMPLE DATE EHDINO 010311 AT 0800 HOURS
FRACTION
CONVENTIONALS
NON-CONVENTIONAL8
VOLAULEB
oo
ACID EXTRACT
BASE-NEUTRALS
METALS
PARAMETER
»OD
TOTAL SUSP. SOLIDS
COD
OIL 1 OREA8E
TOTAL PHENOLS
TOTAL BOLID9
TOTAL DIBS. SOLIDS
TOTAL VOLATILE SOLIDS
VOLATILE DISS. SOLIDS
TOTAL VOL. SU8. SOLIDS
AMMONIA NIIROOEH
TOC
»ENZCNE
111»I-TRICHLOROETHANE
IiI>2-TftlCHLOROETHANE
CHLOROFORM
ETHYL BENZENE
HETHYLENE CHLORIDE
TRICHLOROFLUOROME THANE
TETRACHLOROETHYLENE
TOLUENE
TRICHLOROETHVLENE
2i4t4-TRlCHLOROFHEHOL
PARACHLOROHETA CRE80L
2.4-DICHLOROPHEMOL
2>4-DIHETHYLPHENOL
PENTACHLOROPHENOL
PHENOL
Ii2i4-TRtCHLOROBENZENE
1(2-DICHLOROBENZEME
1>3-DICIILOROBENZENE
li4-DICHLOROBENZENE
FLUORANTHENE
NAPHTHALENE
1>2-SENZANTHRACENE
11>12-BENZOFLUORANTHENE
CHRY8EME
ACENAPHIHYLENE
ANTHRACENE
FLUORENE
PHENANTIIRENE
PYRENE
ANTIMONY
ARSENIC
BERYLLIUM
CADMIUM
INFLUENT
134343
10318*
278088
14874
341
484903
384244
142483
*448i
44004
3378
104*07
TOTAL*
OUT
134233
380041
SS4040
20711
97. f
4*2943
913321
320*14
28343
2*2310
3833
40874
EFFLUENT
14472
6739
37342
H-D
73.1
28*441
28124*
30382
22*17
7444
3277
2047*
PRIMARY
SLUDGE
17410
44371
448*1
3134
3.3
4f044
2344
2*438
728
2B447
93.8
3482
SECONDARY
SLUDGE
122331
324*30
431827
173*7
*.9
334438
2*308
2408*4
4478
234217
304
14*13
4.3
3.4
H-D
37.9
17.4
22.4
.4
44.*
7*.3
2.8
.4
1.2
3.4
4.9
4.0
200
1.3
N-D
3.1
H-D
N-D
*.3
N-D
N-D
N-D
N-D
H-D
N-D
H-D
N-D
N-D
4.3
N-D
1.*
1.1
.5
.4
14.3
2.3
10.4
.3
12.7
13.7
3.2
N-D
N-D
3.3
4.4
N-D
33.*
9.4
.2
N-D
.2
4.2
».8
.1
.1
.2
.1
.1
.3
,4
.9
.2
3.7
4,1
I.I
.3
N-D
14.2
2.2
10.4
,3
11.7
13.1
.3
N-D
H-D
3.3
4.4
N-D
33.0
N-D
N-D
N-D
N-D
H-D
H-D
N-D
N-D
N-D
N-D
N-D
H-D
N-D
N-D
N-D
3,8
N-D
N-D
N-D
N-D
.4
.1
.1
N-D
N-D
N-D
.4
1.*
N-D
N-D
N-D
N-D
N-0
.»
l.»
.2
H-D
.3
.4
4.3
,1
.1
.2
.1
.1
.3
.4
.9
.2
.8
L 0.1
.9
N-D
N-D
N-D
N-D
N-D
N-D
H-D
1.0
N-D
1.3
N-D
H-D
N-D
N-D
N-D
tt-D
3,9
N-D
H-D
N-D
3.4
3.9
N-
N-
N-
N-
N-
N-
N-D
N-D
H-D
1.1
.8
3.4
* TOTAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOVS
POLLUTANTS NOT LISTED HERE NOT DETECTED AT ANY SAMPLE POINT
L-IESS THANI N-D-NOT DEUCTCD.
-------
MASS BALANCE IM f-OUHDB PER DAY
ton SAMPLE PATE ENDiHO BIOIII AT oooo HOURS
FRACTION
HETALS
NON-CONV. HE IALB
a
00
PARAMETER
--.---.——--
CHROMIUM
COPPER
CYANIDE
LEAD
HERCURV
NICKEL
SILVER
ZINC
ALUMINUM
BARIUM
BORON
CALCIUM
COBALT
IRON
MAONEBIUN
HANOANEBE
SODIUM
VANADIUM
INFLUENT
TOTAL*
OUT
11.0
43.»
N-D
.2
N-D
2,3
170
U42
41.4
92.7
14174
1.4
1103
27B»
fl.O
11)333
2.6
m
14'.
41.
L
II.
B.
200
EFFLUENT
12.1
4.1
27. f
N-D
N-D
N-D
.3
39.9
Ml HART
BLUDOE
11.7
11. 1
1.9
10.4
L O.I
4.t
1.1
97.0
SECONDARY
BLUDOE
149
lf.«
3.1
11.9
N-D
f.7
*.•
108
104
7.4
27.1
12019
1.0
7f.2
21B4
42.1
N-D
NOT ItUN
NOT RUN
NOT RUN
HOT HUH
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
HOI RUN
HOT RUM
HOT RUN
HOT RUN
HOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
* TOTAL MASS OUT 18 NOT ADJUSTED KT MASS CONTAINED IN RETURN FLOWS
POLLUTANTS NUT LISTED WERE NOI DETECTED AT ANY SAMPLE POINT
L'USS THANI N-D*NOT DETECTED.
-------
HASS BALANCE IN POUNDS PER DAY
FOR SAMPLE PATE INDIHO 810312 AT 0800 HOURS
FRACTION
CONVENTIONALS
NON-CONVENT IOMALB
1-PICHLOROETHYLENE
lt2-TRANB-PICHLOROETHYLENE
I>2-DICHLOROPROPANE
1»3-OICHLOROPROFYLENE
ETIIYLBENZENE
HETHYLENE CHLORIDE
TRICHIOROFLUOROHETHANE
CHLOROIilBROHOHETHANE
TETRACMLOROE THYLENE
TOLUENE
TftlCHLOROETHVLENC
2r4-PICHLOROPHENOL
2>4-DIHETHYLPHENOL
PHENOL
lf2>4-TRICHLOROBENZENE
lf2-DlCHLOROBENZENE
lt3-DICHLORQBENZENE
11 4-DICHLOROIiENZENE
FLUORANTHENE
NAPHTHALENE
BIS(2-ETHTLHEXYL) PHTHALATE
II112-BENZDFLtlORANTHENE
CIIRYBENE
ANTHRACENE
FLUORENE
PHENANTHRENE
ANMHONY
INFLUENT
l»»747
1 22115
394423
7006
30*
SI2303
38*847
171733
811*3
f033?
3800
1304*3
•4.3
.3
1.3
3.2
.4
.3
32.2
.3
1.0
.3
.3
9.7
43.1
.3
.3
24.3
»3.4
3.2
l.«
4,2
144
N-D
N-D
,3
2.t
N-P
4.1
N-P
N-D
N-P
N-D
N-P
N-P
TOTAL*
OUT
143330
13323?
410443
21128
43,3
338011
3B4I80
180244
44303
II37A3
3314
40314
I.I
N-D
.4
.»
N-P
.9
II. 0
N-P
N-P
N-D
N-D
2.1
8.3
N-P
N-P
3.8
12.0
1.3
2.3
3.1
13.4
11. 8
.4
1.4
.1
.3
14.3
.2
.2
,1
.1
.2
,4
EFFLUENT
13424
10034
7140*
2371
32.3
337043
34341*
47410
38270
»I40
2834
23707
1.1
N-P
.4
.»
N-
N-
10 0
N-
N-
M —
N-P
2.0
8.3
N-D
N-P
3.7
11.4
.3
2.3
3.1
12.4
N-
N-
1 4
N-
H-
4 3
N-
N*
N-
N-
N-P
N-D
PRIMARY
SLUDOE
7733
781*
71221
1372
2.2
10034
2214
341*
473
3144
40.1
2174
N-P
N-P
N-P
H-P
N-P
.3
L O.I
N-D
N-D
N-P
N-P
.1
N-P
N-P
N-P
.1
.4
1.0
N-P
H-D
.8
2.4
.4
N-D
.1
.3
2.3
.2
.2
.1
.1
.2
.4
SECONDARY
SLUDOE
122331
134304
447B13
14*83
?.o
170932
34343
107237
9738
10147*
448
12233
N-D
N-D
N-D
H-D
N-D
N-D
.»
N-D
N-D
N-D
N-D
N-D
N-P
H-P
N-P
N-P
N-P
N-D
N-P
N-D
N-D
f .4
N-P
N-D
N-P
N-D
».7
N-D
N-D
N-D
N-D
N-D
N-D
N-D
N-D
.1
N-D
* TOTAL MASS OUT IS NOT ADJUSTED BY MASS CONTAINED IN RETURN FLOWS
FUtLIJTANIS NOT LISTED WERE NOT DETECTED AT ANY SAMPLE POINT
L--LESS IHAHI N-D-NOT (
-------
MASS VALANCE IM FOUNDS PER PAY
FOR SAMPLE PATE CNDINU 010112 AT oeoo HOURS
FRACTION
NUN-CONV. METALS
O
GO
PARAMETER
ARIEMIC
BERYLLIUM
CADMIUM
CHROMIUM
COWER
CYANIHE
LEAD
MERCURY
NICKEL
SILVER
ZINC
ALUMINUM
•AKIUM
BORON
CALCIUM
COBALT
IRON
MAGNESIUM
MANOANESE
SODIUM
VANADIUM
INFLUENT
TOTAL*
OUT
N-li
M-D
i.r
IS. 4
12.2
25. B
N-D
L O.|
111
2. A
US
1*37
31.*
AI. a
15144
4. a
1031
2370
ft. 7
1.7
1.0
4.0
411
74.4
IB.S
34.4
.4
270
2.4
EFFLUENT
N-D
N-D
H-fl
11.4
«.l
24. »
N-0
L 0.1
28. A
.1
11.4
134
7.7
49,7
12348
2,»
>1.4
2203
42. B
103400
N-D
PRIHART
BLUDOE
.4
L O.I
.4
21.7
14.1
2.2
• .2
L O.I
10.*
I.I
33.4
NOT RUN
NOT RUN
NOT RUN
NOT RUM
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
SECONDARY
BLUDOE
1.
.
1.
Jtt
34.
II.
20.
.
IV.
7.
104
NOT RUN
MOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
NOT RUN
o
•fl
I
« IOIAL MASS OUT IS NOT ADJUSTED »V HAS0 CONTAINED IN RETURN FLOII8
MULUTANT6 NOT LISttD WEKE NOT DfTECTED AT ANY SAMPLE POINT
I-LESS THAN* N-D'NOT DETECTED.
------- |