J1-Northeast_Creek_TMDL_Final

Fecal Coliform Total Maximum Daily Load for the
Northeast Creek Watershed, Durham County, Chatham County and
Wake County
Final Report
July 2003
Cape Fear River Basin
Prepared by:
NC Department of Environment and
Natural Resources
Division of Water Quality
Water Quality Section — Planning Branch %AT
1617 Mail Service Center'
Raleigh, NC 27699-1617 > -
[phone] Ca �

Northeast Creek Fecal Coliform TMDL
INDEX OF TMDL SUBMITTAL
303(d) List Information
State North Carolina
Basin Cape Fear River Basin
303(d) Listed Waters
Name of Stream Description Assessment 8 Digit CU Miles
_unit
Northeast Creek From NC HWY 55 to Durham Co. WWTP WS1V NSW 16-41-1-17- 03030002 2.6
(07)a
Durham Co. WWTP to a point 0.5 mile WS1V NSW 16-41-1-17- 03030002 5.8
downstream of Panther Creek (0.7)b
8 Digit Cataloging Unit(s)
Area of Impairment
WQS Violated
Pollutant of Concern
Sources of Impairment
03030002
7.4 miles
Fecal Coliform
Fecal Coliform
Point source and non -point source from
upstream of SR1100 near Nelson
Public Notice Information
Form of Public Notification:
A draft of the Northeast Creek Fecal Coliform TMDL was publicly noticed though local newspapers, The
Herald -Sun and The Chatham Record, in the Cape Fear River Basin. The notice was also posted in the DQW
web site (http://h2o.enr.state.nc.us/tmdl) for the interested parties. A public meeting was held in Durham
County Agricultural Building on May 27, 2003. A public comment period was through June 5, 2003.
Did notification contain specific mention of TMDL proposal?
Yes
Were comments received from the public?
No
Was a responsiveness summary prepared?
No
i

Northeast Creek Fecal Coliform TMDL
TMDL Information
Critical condition Wet weather throughout the year.
Seasonality Modeled from 1997-2001 to include fluctuations in seasonal
fecal coliform loading.
Development tools Fecal Coliform Routing and Allocation Program (CRAP).
Supporting documents Draft Total Maximum Daily Load for Fecal Coliform,
Northeast Creek (Sub -basin 030605)
TMDL(s)
Loading allowed at critical condition:
Waste Load Allocation (WLA)
Load Allocation (LA):
Margin of Safety (MOS):
TMDL (WLA+LA+MOS):
1.12E+I I Colonies per day.
2.40E+11 Colonies per day.
5.06E+10 Colonies per day.
4.03E+11 Colonies per day.
Total Maximum Daily
Sources
Fecal
Load (TMDL)
Coliform
Loading
Reductions
Wasteload
WWTP
0%
Allocation (WLA)
MS4
92%
Load Allocation (LA)
Low Intensity Development
94%
High Intensity Development
92%
Herbaceous Land
90%
Wildlife
0%
ii

Northeast Creek Fecal Coliform TMDL
TABLE OF CONTENTS
INDEX OF TMDL SUBMITTAL............................................................................................ i
TABLE OF CONTENTS.............................................................................................................. ill
1.0 INTRODUCTION........................................................................................................1
1.1 Watershed Description..................................................................................................2
1.2 Water Quality Target: North Carolina Water Quality Standard..................................5
1.3 Water Quality Assessment............................................................................................5
2.0 SOURCE ASSESSMENT...........................................................................................8
2.1 Point Source Assessment..............................................................................................9
2.2. Non -point Source Assessment...................................................................................10
3.0. MODELING APPROACH.............................................................................................16
3.1 Modeling Framework...................................................................................................16
3.2 Model Setup................................................................................................................17
3.3 Model Calibration.......................................................................................................19
3.4 Model Uncertainty.......................................................................................................23
3.5 Model Output...............................................................................................................23
4.0 ALLOCATION..........................................................................................................
26
4.1. Total Maximum Daily Load.......................................................................................26
4.2 Seasonal Variation.......................................................................................................28
4.3 Margin of Safety(MOS).............................................................................................29
4.4. Waste Load Allocation...............................................................................................29
4.5 Load Allocation (Non -point Source)...........................................................................30
5.0 SUMMARY AND FUTURE CONSIDERATIONS.................................................31
5.1 Monitoring...................................................................................................................32
5.2 Implementation............................................................................................................
32
6.0 PUBLIC PARTICIPATION......................................................................................33
7.0 REFERENCES................................................................................................................34
Appendix 1. Fecal Coliform in the Ambient Station (B3660000).........................................36
Appendix 2. Flow Recorded by USGS at the ambient Station(B3660000).........................
39
Appendix 3. Relationship between Flow and Velocity at the Ambient Station (3660000)..47
Appendix 4. Fecal coliform at Durham West Water Treatment Plant (WWTP)..................48
Appendix 5. Fecal Coliform Sampling in Durham County, NC...........................................63
Appendix 6. Partial List of General NPDES Permits in Northeast Creek Watershed . ......... 64
Appendix 7. Estimated high fecal coliform (❑ 400) occurrence...........................................65
Appendix 8. Public notice of draft Northeast Creek Fecal Coliform TMDL ......................67
iii

Northeast Creek Fecal Coliform TMDL
1.0 INTRODUCTION
The North Carolina Division of Water Quality (DWQ) has identified an 8.4 mile segment of
Northeast Creek in the Cape Fear River Basin as impaired by fecal coliform bacteria
(NCDENR 2003). The impaired segments due to fecal coliform bacteria are located from 2.6
miles upstream of N.C. Hwy 55 to Durham County WWTP and 5.8 miles from Durham
County WWTP to a point 0.5 mile downstream of Panther Creek. About 4.7 miles of upper
Northeast Creek is designated as class C' water and the remaining length is designated as a
class WS-IV water 2. These sections of the stream are located in sub -basin 030605.
The 303(d) process requires that a Total Maximum Daily Load (TMDL) be developed for
each of the waters appearing in category 5 of the 2002 Integrated Report. The objective of a
TMDL is to allocate allowable pollutant loads to known sources so that actions may be
taken to restore the water to its intended uses (USEPA, 1991). Generally, the primary
components of a TMDL, as identified by USEPA (1991, 2000a) and the Federal Advisory
Committee (FACA, 1998) are as follows:
Target identification or selection of pollutant(s) and end-point(s) for consideration. The
pollutant and end -point are generally associated with measurable water quality
related characteristics that indicate compliance with water quality standards. North
Carolina indicates known pollutants on the 303(d) list.
Source assessment. All sources that contribute to the impairment should be identified and
loads quantified, where sufficient data exist.
Assimilative capacity estimation or level of pollutant reduction needed to achieve water
quality goal. The level of pollution should be characterized for the water body,
highlighting how current conditions deviate from the target end -point. Generally,
this component is identified through water quality modeling.
Allocation of pollutant loads. Allocating pollutant control responsibility to the sources of
impairment. The waste load allocation portion of the TMDL accounts for the loads
associated with existing and future point sources. Similarly, the load allocation
portion of the TMDL accounts for the loads associated with existing and future non -
point sources, storm water, and natural background.
Margin of Safety. The margin of safety addresses uncertainties associated with pollutant
loads, modeling techniques, and data collection. Per EPA (2000a), the margin of
1 Class C waters are freshwaters that are protected for secondary recreation, fishing, aquatic life including
propagation and survival of wildlife.
2 Class WS-IV waters are freshwaters that are protected for water supply, secondary recreation, fishing, and
aquatic life, including propagation and survival of wildlife.

Northeast Creek Fecal Coliform TMDL
safety may be expressed explicitly as unallocated assimilative capacity or implicitly
due to conservative assumptions.
Seasonal variation. The TMDL should consider seasonal variation in the pollutant loads
and end -point. Variability can arise due to stream flows, temperatures, and
exceptional events (e.g., droughts, hurricanes).
Section 303(d) of the CWA and the Water Quality Planning and Management regulation
(USEPA, 2000a) requires EPA to review all TMDLs for approval or disapproval. Once
EPA approves a TMDL, then the water body may be moved to category 4a of the Integrated
Report. Water bodies remain on category 4a of the list until compliance with water quality
standards is achieved. Where conditions are not appropriate for the development of a
TMDL, management strategies may be implemented in an effort to restore water quality.
The goal of the TMDL program is to restore designated uses to water bodies. Thus, the
implementation of bacteria controls will be necessary to restore uses in Northeast Creek.
Although an implementation plan is not included as part of this TMDL, reduction strategies
are needed. The involvement of local governments and agencies will be critical in order to
develop implementation plans and reduction strategies. DWQ will begin contacting local
governments and agencies about implementation strategies during public review of this
TMDL.
1.1 Watershed Description.
Northeast Creek flows from Durham to Chatham counties in the piedmont region of North
Carolina (Figures Iand 2). It is a tributary to the New Hope River arm of B. Everett Jordan
Reservoir (Sub -basin 030605) in the Cape Fear River Basin. Northeast Creek joins New
Hope Creek in the northeast corner of Chatham County, NC. The hydraulic length of
Northeast Creek is approximately 16 miles and the creek has a drainage area of
approximately 47 square miles. Land cover based on 1993-95 satellite data in the watershed
is primarily forest (86%), high intensity development land (6.5%), low intensity
development land (1.5%), managed herbaceous land (4.5%), unmanaged herbaceous land
(0.3%), cultivated land (0.2%) and water body 1 % (Figure 3). The dense coverage of the
developed
2

Northeast Creek Fecal Coliform TMDL
N
W E
S
1:176188
Index:
❑ Coalition Station
O Ambient Station
6 Durham-RTP WWTP
Figure 1. Northeast Creek watershed showing monitoring stations and Durham Triangle WWTP
3

Northeast Creek Fecal Coliform TMDL
Chatham Co.
r
Wake Co.
E
Figure 2. Location of the City of Durham MS4 within the city boundary in Northeast Creek Watershed
0

Northeast Creek Fecal Coliform TMDL
lands is often considered forestland. The annual average flow of the creek at the ambient
station near Nelson in Durham, is approximately 31.5 cubic feet per second (cfs), with a
7Q10 of 1.8 cfs (Weaver and Benjamin, 2001). The Creek is prone to become dry during
drought conditions (From DWQ staff s observation in 2002). It could be because the creek
drains Triassic Basin soils, which have high clay content and are slowly permeable sub -soils
with moderate to very high shrink -swell potentials. The watershed includes drainage from
the City of Durham, Research Triangle Park, Town of Cary, and the northeast portion of
Chatham County. Therefore, the watershed encompasses three counties — Durham County,
Wake County, and Chatham County.
1.2 Water Quality Target: North Carolina Water Quality Standard.
The North Carolina fresh water quality standard for Class WS-IV and C waters for fecal
coliform (T15A: 02B.0211) states:
Organisms of the coliform group: Fecal coliforms shall not exceed a geometric mean of
2001100mL (MF count) based upon at least five consecutive samples examined during
any 30-day period, nor exceed 4001100mL in more than 20 percent of the samples
examined during such period; violations of the fecal coliform standard are expected
during rainfall events and, in some cases, this violation is expected to be caused by
uncontrollable nonpoint source pollution; all coliform concentrations are to be
analyzed using the membrane filter technique unless high turbidity or other adverse
conditions necessitate the tube dilution method; in case of controversy over results, the
MPN 5-tube dilution technique will be used as the reference method.
The in -stream numeric target, or endpoint, is the restoration objective that is expected to be
reached by implementing the specified load reductions in the TMDL. The target allows for
the evaluation of progress towards the goal of reaching water quality standards for the
impaired stream by comparing the in -stream data to the target. In the Northeast Creek
watershed, the water quality target is the 30-day geometric mean concentration of 200
colonies /100ml with no more than 20% of the samples in the same period exceeding 400
colonies / 100 ml.
1.3 Water Quality Assessment.
The DWQ monitors a suite of water quality parameters, including fecal coliform bacteria, at
ambient stations throughout the state on a monthly basis. There is one DWQ ambient station
5

Northeast Creek Fecal Coliform TMDL
(B3660000) in this watershed located at SR 1100 near Nelson (Figure 1). Fecal coliform
levels at SR1100 are responsible for the 303(d) listing of a portion of Northeast Creek.
UMH
_ nnu 0.29%W
F
85.77%
■C OF ❑HID ❑LID ■MH ■UMH ■W
Figure 3. Distribution of land use in the Northeast Creek watershed. C = Cultivated land,
F = Forested land, HID = High intensity developed land, LID = Low intensity developed
land, MH = Managed herbaceous land, UMH = Unmanaged herbaceous land, and W =
Water body.
The Upper Cape Fear River Basin Association monitored the water quality at two additional
coalition stations - B3300000 and B3670000 near SR1102 (Sedwick Rd) and SR1731
(O kelly Church Rd) respectively during the years 2000 through 2002 (Figure 1). The DWQ
staff also monitored the water quality at the stations during 2002. The monthly fecal
coliform data is available for the years 2000 through 2002. The fecal coliform data
collected at these two stations offers the unique opportunity to compare the longitudinal
distribution of the bacterial concentration along the Northeast Creek. Figure 4 indicates that
the average bacterial concentration (598 counts/100ml) at the ambient station (133660000)
was nearly double the concentration (259 counts/ 100ml) at its receiving station (133300000)
in the year 2000. Furthermore, the bacterial concentration in the effluent discharged from
ro

Northeast Creek Fecal Coliform TMDL
the Durham Triangle WWTP to the ambient station was comparatively low, averaging 60
counts per 100 ml, which is below the DWQ standards. A similar pattern of bacterial
concentration is also observed in the year 2001 and 2002.
The substantial spike of fecal concentrations at the ambient station (B3660000) could be due
to a sewer pipe leaking or some other source between the coalition station (B3300000) and
the ambient station (B3660000). The influence of this unknown source, however, gradually
decreased moving downstream, as evident at the down stream coalition station (133670000).
700
600
500
E
0
0
c
400
R
N
E
U
300
E
0
m
200
100
0
Fecal Coliform Distribution Along the Northeast Creek
598
454
259
232
90
200
138 154
56 62 52
B3300000 WWTP B3660000 B3670000
Monitoring Stations
Dyear2000 Oyear2001 ■year2002
Figure 4. Geometric mean of fecal colifrom concentrations in the ambient and coalition
stations and in the Durham Triangle WWTP for the years 2000 through 2002, from
upstream to downstream.
DWQ staff also conducted an additional study at the ambient station (133660000) to
determine compliance with the fecal coliform standard. Weekly samples were collected
during November 1999 and during May, June, August, and September 2000. These
VA

Northeast Creek Fecal Coliform TMDL
additional samples also provided opportunity to calculate a 30-day geometric mean using 5
or more samples during that period. In most of the periods, the 30-day geometric mean of
the fecal coliform concentration at the ambient station remained considerably higher than
200 colonies / 100 ml. The 30-day geometric mean fecal coliform concentrations for 1997
through 2001 are shown in Figures 6-8.
In general, the fecal bacterial levels at the ambient station (133660000) are typical of fecal
coliform levels in many urban areas, with frequent concentration spikes. Out of 59 samples
collected during the study period at this station (1997 through 2001), 24 were exceeding 400
colonies / 100 ml (41 %). The monthly fecal coliform concentrations for 1997 through 2001
are shown in Appendix I.
The USGS flow station monitored stream discharges (cfs) every 15 minutes at the ambient
station (B3660000). These monitored discharge data were used to evaluate potential
compliance with the standard and to aid modeling studies. The discharge data is presented
in Appendix 2.
2.0 SOURCE ASSESSMENT
The source assessment characterizes the known and suspected sources of a pollutant to the
impaired water body. These sources will be represented within the water quality model for
the water body, whether explicitly or implicitly. Generally, sources of fecal coliform
bacteria may be point or non -point in nature. Point sources are typically those regulated
under the National Pollution Discharge Elimination System (NPDES) program. Wastewater
facilities have permitted discharges for which the DWQ has significant information.
Continuous discharge and/or wastewater NPDES facilities measure fecal coliform levels in
the effluent at a frequency based on facility class and waste type. Non -point sources are
diffuse sources that typically cannot be identified as entering a water body at a single
location. These sources may involve land activities that contribute fecal coliform bacteria to
surface waters as a result of runoff producing storm events. The following sections describe
point and non -point sources of fecal coliform bacteria in the Northeast Creek watershed.

Northeast Creek Fecal Coliform TMDL
2.1 Point Source Assessment.
There are currently about 31 NPDES permits within the Northeast Creek watershed.
Twenty-eight of them are individual and general permits. Monitoring of water quality under
these permits is carried out once a year and measurement of fecal coliform is not mandatory.
So, the data from these permits are not considered for this study. The partial list of these
permits is presented in Appendix 6. Three out of the 31 permits are under regular NPDES
permit, where measurement of fecal coliform is mandatory (Table 1). One of them is
regulated under storm water program, which is commonly known as Municipal Separate
Storm Sewer System (MS4).
In 1990, EPA promulgated rules establishing Phase 1 of the NPDES storm water program.
The Phase I program for MS4 requires operators of medium and large MS4s, that is, those
that generally serve populations of 100,000 or greater, to implement a storm water
management program as a means to control polluted discharges from these MS4s. The
Storm Water Phase II Rule extends coverage of the NPDES storm water program to certain
"small" MS4s, which is not already covered by the Phase I program as a medium or large
MS4. The Phase II takes a slightly different approach to how the storm water management
program is developed and implemented (US EPA 2000).
EPA guidance mandates that all the urban areas that are documented as MS4 must be
categorized as point source (US EPA 2000). The two entities that are permitted through
Phase I of NPDES storm water program to discharge in the Northeast Creek watershed are
the City of Durham (NCS000249) and the North Carolina Department of Transportation
(NCS000250). As part of Phase II of the NPDES storm water program, Durham County,
which has jurisdiction over some land and storm pipes in the watershed, will be added.
In the Northeast Creek watershed, all the MS4 areas were located in Durham County. Out
of the 940 hectares of the developed lands in WS1 and WS2 (Table 5), about 223 hectares
(24%) of the lands were estimated to be draining to the MS4 areas. Of the 223 hectares, the
City of Durham MS4 represented 197 hectares and NC DOT MS4 represented 26 hectares (a
best estimation from Mr. John Cox, City of Durham).
9

Northeast Creek Fecal Coliform TMDL
Detailed information regarding the discharge rates and fecal concentration is not readily
available for storm water in the MS4 areas. The load from the MS4 areas is therefore
estimated by multiplying the total load discharged through the developed lands from the
percentage (24%) occupied by the MS4 areas.
McCarthy and Associates and the Durham Triangle WWTP are regulated under the NPDES
system. However, the McCarthy and Associates is not discharging and hence, it is not
considered in this study. The Durham Triangle WWTP discharges domestic and industrial
wastewater. The discharge is monitored for fecal coliform on a daily basis. The daily
average fecal coliform load from the facility is presented in Appendix 4.
Table 1. NPDES Permits in the Northeast Creek Watershed
Permitted flow
Actual flow (a)
Facility =
Permit number
(MGD)
(MGD)
Waste type
McCarthy and
NC0085260
N/A
N/A
Industrial
Associates
Durham Triangle
NC0026051
6
3.24
Domestic +
WWTP
Industrial
MS4
City of Durham
NCS000249
NA
NA
Domestic +
NC DOT
NCS000250
NA
NA
Industrial
(a) Average annual flow for calendar
year 2000.
2.2. Non -point Source Assessment
Fecal coliform bacteria non -point sources include those sources that cannot be identified as
entering the water body at a specific location. Non -point source pollution can include both
urban and agricultural sources, and human and non -human sources (Table 2). The non -point
sources of fecal coliform bacteria in Northeast Creek include wildlife, livestock (land
application of agricultural manure and grazing), urban development (stormwater runoff,
including sources from domestic animals), failing septic systems, and sewer line systems
(illicit connections, leaky sewer lines and sewer system overflows).
10

Northeast Creek Fecal Coliform TMDL
Table 2. Potential Source of Fecal Coliform Bacteria in Urban and Rural Watersheds.
(Source: Center for Watershed Protection, 1999)
Source Origin Type
Source
Human Sources Sewered watershed
Combined sewer overflows
Sanitary sewer overflows
Illegal sanitary connections to
storm drains
Illegal disposal to storm drains
Non-sewered watershed
Failing septic systems
Poorly operated package plant
Landfills
Marinas
Non -human Sources Domestic animals and
urban wildlife
Dogs, cats
Rats, raccoons
Pigeons, gulls, ducks, geese
Livestock and rural wildlife
Cattle, horse, poultry
Beaver, muskrats, deer,
waterfowl
Hobby farms
2.2.1 Livestock.
In order to incorporate the actual amount of fecal coliform deposited from livestock, a
survey was conducted with the help of County Agents, Mr. Henry Outg (Chatham Co.), Mr.
Steve Woodruff (Wake Co.), and Ms. Karen McAdams (Durham Co), to enumerate the
approximate head count of livestock in the Northeast Creek watershed. The estimated head
count from this survey is presented in Table 3.
Table 3. Estimated Livestock in the Northeast Creek
Watershed.
Livestock I Durham Co. Wake Co. Chathem Co
Beef Cows 80 0
10
Horses 175 35
20
All of the beef cows are managed under the NC Agriculture Cost Share Program. The
program prohibits the grazing of the cattle near the stream. As the result, during a field
survey on January 15, 2000, DWQ staff and County agent, Ms. Karen McAdams, observed
11

Northeast Creek Fecal Coliform TMDL
no cattle grazing along Northeast Creek. They observed mainly horses grazing in the
managed herbaceous land near the creek.
Furthermore, DWQ staff observed that more than half of the herbaceous land (mostly grass
lands and crop lands), as identified by the 1996 land use data used for this study, have been
converted to low intensity development. It is, therefore, assumed that the impact of fecal
coliform due to the animal operations in the watershed should have been reduced by one
fourth of the actual load rates. The actual loading rates for livestock in the Northeast Creek
watershed were estimated to be 3000 to 7000 colonies per 100 ml. Fecal coliform
concentrations from grazed pasture runoff have been measured in the range of 120-1.3E+6
colonies/100 ml (Doran et al. (1981). The presence of cattle on rangelands increased fecal
coliform in stream concentrations from 0 to 2500 colonies per 100 ml (Khaleel et al.1980).
2.2.2. Domestic Animals
Dogs and cats are the major domestic animals in the watershed. As per the Durham County
Animal Control database, the population of dogs and cats in the county is estimated to be
37,396 and 19,230 respectively. In a study conducted by Hyer et. al, 2001, the bacterial
loads due to dog waste accounted for nearly 10 percent of the total bacterial load in three
creeks of Virginia, Accotink Creek, Blacks Run, and Christians Creek. In Melbourne,
Australia, dogs produced about 90 metric tons of feces each day - equivalent to the amount
of feces produced daily by 90,000 people
(http://www.esb.utexas.edu/nrm200l/dogdoo/WaterQuality(JJ)/Default.htm). Therefore a
separate study of the fecal loads due to dogs and cats is essential for cities like Durham.
During a survey, DWQ staff observed a considerable amount of dog waste along the creek
near residential areas. During a rainfall runoff event, a portion of the fecal material, which
contains coliform bacteria, is transported to the creek. Open lots used heavily by animals
have the greatest potential for bacteria loads to surface water. In addition, when animals
have direct access to streams, feces may be deposited directly into a stream. It is, therefore,
assumed that out of the total fecal coliform load estimated for urban development, 10% of
the load would have come from domestic animals.
12

Northeast Creek Fecal Coliform TMDL
Once the bacteria reach a water body, environmental factors influence the extent of their
growth and decay. Physical factors such as photo -oxidation, adsorption, flocculation,
coagulation, sedimentation, and temperature will have a great influence on the bacteria
populations (USEPA, 1985). Some studies have suggested a significant positive correlation
between bacteria, stream flow, and stream temperature along with a negative correlation
with pH, specific conductance, and disolved oxygen (Wilhelm and Maluk, 1998; and Clark
and Norris, 1999).
2.2.2. Failed Septic Systems
Failing septic systems have been cited as a potential source of fecal coliform bacteria to
water bodies (DEH, 2000). About 18 percent of the residents in the Northeast Creek
watershed utilized septic systems (Table 4) and there were about 2.3 people per household
per septic system. A GIS map developed by the Soil Science Department, North Carolina
State University showing the spatial distribution of houses with septic and sewer systems in
the three counties (Durham, Chatham, and Wake) was utilized to estimate the number of
septic and sewer systems in the watershed. The number of houses with septic and sewer
systems in the counties were first divided by the respective areas of the counties. The
houses per area were then multiplied by the area of the watershed within each county to
estimate the total houses with sewer and septic systems in the watershed.
Table 4. Summary of Septic Usage in Northeast Creek Watershed for 2000
Watershed/County
Housing units
Percent of Housing Units Utilizing:
Sewer Septic Other
NE Creek Watershed
43,910*
81
18
1
Durham
89,015
88
11
1
Chatham
19,741
26
73
1
Wake
242,040
84
15
1
*Estimated based on the housing distribution in the three counties.
Frequent failures of the septic systems are common in the Durham County. This argument
is clearly made public by the daily NC newspaper, The News & Observer, on January 3, and
January 10, 2002. The City of Durham conducted field sampling of septic and sand filter
effluent during 1999 and 2000. The concentration of effluent fecal coliform bacteria due to
13

Northeast Creek Fecal Coliform TMDL
septic and sand filter effluent failure ranges from 11 to 490,000 counts/ 100ml based on
study conducted by City of Durham (Appendix 5). These data were used as a basis for fecal
coliform loads from failing septic systems for this study.
2.2.3 Urban Development/Sanitary Sewer Overflows/WWTP Residual Land Application.
Fecal coliform bacteria can originate from various urban sources. These sources include pet
waste (discussed above), runoff through stormwater, sewers, illicit discharges/connections
of sanitary waste, leaky sewer systems, and sewer system overflows (Table 2). The sewage
pipelines to the WWTP run along Northeast Creek. In a record maintained by City of
Durham, the sewer pipe leaked four times in the year beginning May 2001 from the
residential and commercial properties and one time from the City Sanitary Sewer System.
Failures of connections between the sewer pipelines, or any leak from the pipe, could result
in profound fecal coliform loads to the creek.
Storm water runoff is the main carrier of solids, chemicals, and bacteria from urban sources,
including cross -connections with sanitary sewers. Various studies suggest that fecal coliform
counts in urban storm water typically range from 20 to 240,000 units per 100 ml (Farrell -
Poe et al., 1997, Khaleel et al., 1980, and Canale et al., 1993). The magnitude of the
bacterial concentration substantially increases with density of urbanization. Further
concentrations increase substantially during wet weather conditions. For example, dry
weather fecal coliform concentrations in Onondaga Lake and its seven tributaries in
metropolitan Syracuse, NY, ranged from 108 to 25, 525 colonies per 100 ml throughout the
summer of 1987 (Canale et al., 1993). Whereas, wet weather concentrations in the tributaries
ranged from more than 8,000 to 240,000 colonies per 100 ml. In general, significantly
higher colonies (11100,000 colonies / 100 ml) suggest the presence of cross connections with
sanitary sewers, which should be identified and corrected (Marsalek, 2002).
Because of the huge variation of fecal coliform concentration in urban storm water due to
interactions between the seasonal weather pattern and different urban characteristics, a
specific quantification of the fecal concentration in urban storm water for modeling purposes
is difficult. Due to lack of data on site specific fecal coliform loading from urban
14

Northeast Creek Fecal Coliform TMDL
development in the Northeast Creek watershed, the estimation of fecal coliform loading is
limited to best professional judgement based on the above studies. Marsalek (2002) suggests
that fecal coliform concentrations in urban storm water, where sewer cross connection
leaking is a problem, will exceed 100,000 colonies per 100 ml. Therefore, it is assumed that
the fecal concentrations in wet weather and dry weather storm water will be 50,000 and
30,000 colonies per 100 ml respectively, where frequent occurrences of sewer overflows
were observed. The wet weather period for this study was defined as the four consecutive
days following a storm event that produced surface runoff. Remaining days were labeled as
dry weather conditions.
These values were used to estimate total fecal coliform load from low intensity development
and high intensity development. These values were, however, adjusted during the model
calibration.
2.2.4 Wildlife (Background Source).
Wildlife deposit fecal material in forested, wetland, and herbaceous areas, which can be
transported to a stream in a storm event. Deposition of fecal coliform from wildlife
populations is natural. Therefore, wildlife is considered as a background source of fecal
coliform bacteria for this study.
Wildlife in the Northeast Creek watershed includes deer, raccoons, squirrels, birds, and
waterfowl. As population estimates of raccoons, squirrels, birds, waterfowl and other
animals are not readily available, the wildlife fecal coliform contribution was accounted for
in the deer population. The deer population was estimated to be 15 to 30 animals per square
mile in the watershed (source: http://www.ncwildlife.org/pg07_WildlifeSpeciesCon). The
upper limit of 30 deer per square mile was chosen to account for deer and other wildlife in
the watershed. The fecal coliform loading rate assigned to deer was estimated to be 50 to
100 colonies per 100 ml. The Center for Watershed Protection (1999) has cited a fecal
coliform concentration range of 10-100 colonies per 100 ml for forest runoff.
15

Northeast Creek Fecal Coliform TMDL
3.0. MODELING APPROACH
3.1 Modeling Framework.
The watershed model named "The Coliform Routing and Allocation Program (CRAP)" was
selected for fecal coliform TMDL development for the Northeast Creek watershed. The
watershed model is designed to support the USEPA's protocol for estimating TMDL
calculation, allocation, and implementation. The model is a simple, flexible, steady-state
modeling tool. The model can be applied in a variety of watersheds for which there is a
limited available data. CRAP is a customized ArcView project, written in Avenue,
ArcView's scripting language. Output from the model is intended to represent `typical'
instream fecal coliform concentrations within a given time step, for predefined design
(critical) conditions.
The CRAP model estimates fecal loads for each source in each watershed using the
concentration based method with the equation 1:
L=C*Qlc*f ---
(1)
Where,
L = fecal load (cfu/day)
C = `typical' fecal concentration specified by the user(cfu/100mL). The user might choose
to think of this value as the fecal concentration measured in a stream draining a watershed
containing just the single source -associated land cover type.
Qlc = flow contributed by the source associated land cover within a given subwatershed (cfs)
f = factor to convert units of concentration and flow to cfu/day = 24,465,755.
The model estimates instream fecal coliform concentration by routing the total loads from
each sub -watershed downstream taking into account any variation in fecal decay rate
between sub -watersheds. The model utilizes the first order decay equation to estimate the
decay rate:
xt
Ct —Coe-------------------------------------------------------(2)
Where,
Ct is the coliform concentration (colonies/100 ml) at time t.
Co is the initial coliform concentration (colonies/100 ml).
k is the decay rate constant (per day).
16

Northeast Creek Fecal Coliform TMDL
t is the exposure time (days).
Generally, the decay rate (k) varies from 0 to 1.0 per day (Herr et al., 2000). In this study,
the decay rate was used as 0.1 per day.
The exposure time is estimated by dividing the travel distance by stream velocity. The
model estimates the stream velocity using the power function equation:
V=aQb----
---------------(3)
Where,
V is the stream velocity (ft per sec).
Q is the stream flow (cft per sec).
a is the flow coefficient (unitless constant).
b is the exponent coefficient for flow (unitless constant).
The constant coefficients, a and b, were estimated to be 0.32 and 0.24 respectively. The
estimation was done using the instream velocity measured by USGS at the ambient station
(133660000). The measured velocity is presented in the Appendix (3).
3.2 Model Setup.
The Northeast Creek watershed was delineated using the watershed delineation tool built in
the model. A total of six sub -watersheds (WS 1 to WS6) were delineated based on the Reach
file 3 (RF3) stream coverage for the Northeast Creek watershed (Figure I). The total
drainage area of the watershed was estimated to be 12206 hectares (47 square miles) with
hydraulic length of 16 miles (Table 5).
The dominant land cover in the watershed was forested lands. The second dominant land
use was developed lands. The two watersheds, WS1 and WS2, were within Durham County,
including City of Durham and Research Triangle Park and therefore, were dominated by
developed lands. Industrial and commercial developments were located primarily in the
Research Triangle Park. The rest of the watershed was dominated by herbaceous land.
The water quality data and flow data respectively collected by DWQ and USGS at the
ambient monitoring station (133660000) were utilized to calibrate the model. The station was
located in WS2 at about 3 miles below the WS1 (Figure 1).
17

Northeast Creek Fecal Coliform TMDL
Table 5. Land cover characteristics of each sub -watershed in the Northeast Creek
watershed.
Parameters
WS1
WS2
WS3
WS4
WS5
WS6
Total
A. Land use (ha)
Cultivated
5.52
0.00
5.77
5.18
14.99
0.01
31.47
Forest
3506.32
1369.39
2415.58
580.37
2.55.58
541.81
10469.04
Development
❑ High Intensity
704.74
45.47
24.47
00
23.98
0.63
799.29
❑ Low Intensity
190.90
0.00
3.76
0.00
0.00
0.00
194.65
Herbaceous
❑ Managed
179.18
26.43
89.70
6.93
203.84
42.67
548.75
❑ Unmanaged
30.49
0.00
4.87
0.00
0.00
0.00
35.36
Water body
44.67
34.20
25.67
3.09
9.91
9.74
127.27
Total
4661.82
1475.45
2569.81
598.57
2308.29
594.85
12205.83
Stream Length
7.30
4.35
6.37
2.96
5.29
1.34
28.00
(Hydraulic mile)
3.2.1 Wet Weather Versus Dry Weather Fecal Coliform Loading
In this study, it is assumed that surface runoff would be generated in excess of infiltration
capacity of soil surface (maximum rate at which the soil can absorb water through the soil
surface at the time of entry) after each rainfall event. The infiltration capacity is determined
by soil type and moisture content. The soil type in the Northeast Creek watershed is Triassic
soil, which has comparatively low infiltration capacity due to heavy clay layers in the soils.
Owing to presence of clay, soil moisture holding capacity of the soil is reasonably high.
Therefore, wet weather conditions for the watershed were defined as three consecutive days
since the first flow rate increased at the USGS gauge station located at SR1100. The
increment was examined after subtracting the total flow from the flow from the WWTP to
account seepage from the watershed lands. Dry weather accounted for all the remaining
days. There were 59 observed data at SR1100, of which 36 were estimated to be dry
weather and the remaining 23 were to be wet weather period. Similarly, out of the 1826

Northeast Creek Fecal Coliform TMDL
simulation days, 846 days were estimated to be wet weather and the remaining 980 were dry
weather during the study periods.
A partial correlation between flow and fecal coliform concentration during the wet weather
and dry weather period was estimated. The correlations were 0.47 and 0.17. The result
suggests that the correlation was significantly higher during wet weather periods, signifying
that the assumption of the weather period was acceptable.
3.3 Model Calibration.
The watershed model was calibrated with fecal coliform concentrations observed at the
ambient station (B3660000). Since the station was located above the outlet of WS2, the
concentration of fecal coliform at the station was estimated using a proportional decrease in
concentration between the inlet and the outlet of WS2. The formula used for the estimation
of the concentration at the ambient station is as follows:
((Ci — Co)/Dio)*Doa) + Co------------------------------------(4)
Where,
Ci = Concentration at the inlet of WS2.
Co = Concentration at the outlet of WS2.
Dio = Hydraulic distance of Northeast Creek in WS2 = 4.35 mile.
Doa = Hydraulic distance of ambient station from the outlet = 1.43 mile.
In the calibration process, the decay rate of the fecal coliform bacteria in the stream was set
to 0.1. The input parameters estimated in § 2.2.3 for urban development were also further
adjusted to associate the estimated fecal coliform concentration with the observed
concentration. The adjusted concentrations were 40,000 colonies and 55,000 colonies per
100 ml of water during dry weather and wet weather periods respectively. Except for the
first simulation year, 1997, an acceptable association between the simulated fecal coliform
bacterial concentration and observed bacterial concentration was observed when the
estimated parameters were adjusted for wet weather and dry weather periods (Figure 5).
19

Northeast Creek Fecal Coliform TMDL
100000
10000
E
0
0
r 1000
a
100
E
L
O
0
Date
■Observed ♦Simulated
Figure 5. Observed vs Simulated fecal coliform concentration at the ambient station,
B3660000.
The association was further comprehensible when the observed and simulated values were
examined by estimating 30-day geometric mean (Figures 6, 7, and 8). This association could
not be examined for the simulated five-year period since minimum of 5 samples a month is
required for the comparison. The DWQ ambient monitoring station only has fecal coliform
samples on a monthly basis. Therefore, the DWQ staff conducted a special study program
to collect five samples in 30 days at the DWQ ambient monitoring site (SR 1100) during the
summer periods of 1999 and 2000. These data were merged with the regular ambient data to
have comparable geometric mean. The resulting 30-day geometric mean of the fecal
coliform concentration is presented in Figures 6-8.
20

Northeast Creek Fecal Coliform TMDL
E
1000
............................
100
10
1! '
11 /06/99 11 /11 /99 11 /16/99 11121 /99 11 /26/99 12/01 /99 12/06/99 12/11 /99 12/16/99
Dates
• Observed ■ Simulated
Figure 6. Rolling 30-day geometric mean of observed and predicted fecal coliform
concentration at the ambient station (133660000) for 1999.
The association between the 30-day geometric mean of observed and predicted fecal
coliform concentrations was somewhat weak for 1999 (Figure 6). The model estimated
considerably higher fecal coliform concentration than the observed concentration. It could
be either due to the estimation of higher initial fecal coliform concentration for the model
input in order to be consistent with the following years' developments in the watershed, or
could be due to model uncertainty (discussed below). However, the association was
significantly improved in the following years 2000 (Figures 7 and 8).
21

Northeast Creek Fecal Coliform TMDL
1000
E
0
0
fR
100
3
O
U
E
L
O
W
p 10
U
m
u
d
LL
1
06/03/00 06/08/00 06/13/00 06/18/00 06/23/00 06/28/00 07/03/00 07/08/00
Date
• Observed ■ Simulated
Figure 7. Rolling 30-day geometric mean of observed and predicted fecal coliform
concentration at the ambient station (B3660000) for the early summer, 2000.
1000
E
0
0
w 100
c
3
O
V
E
L
O
L) 10
u
d
LL
1 4--
09/01 /00
i i i i � � � � � i i i i • � • i i • • ■ •
09/06/00 09/11/00 09/16/00 09/21/00 09/26/00 10/01/00
Date
♦ Observed ■ Simulated
Figure 8. Rolling 30-day geometric mean of observed and predicted fecal coliform
concentration at the ambient station (B3660000) for the late summer, 2000.
22

Northeast Creek Fecal Coliform TMDL
3.4 Model Uncertainty
The weak agreement between modeled and observed fecal coliform concentrations as
described in Section 3.3 could be due in part to the high degree of uncertainty associated
with predicting fecal coliform bacteria. The inability to accurately predict specific observed
fecal coliform concentrations can be attributed to model error, lack of sufficient information
in source assessment, gaps in our scientific knowledge, natural variability in instream fecal
coliform concentrations, field and laboratory measurement error, and lack of current site -
specific model input parameters including decay rate, flow, and land use information. The
model, CRAP, selected to guide initial decision making, is not able to characterize
prediction uncertainty. The model estimates daily average fecal coliform concentrations
based on land use information and stream flow. The model does not consider the
contribution of stream temperature to the fecal decay rate. Also, because of lack of a site -
specific information, professional judgement and literature values were used to calculate the
fecal coliform loading from the various land uses. Therefore, the model results should be
interpreted in light of the model limitations and prediction uncertainty.
3.5 Model Output
3.5.1 Existing Loading
The model outputs indicate that the primary source of fecal coliform bacteria loads to
Northeast Creek is the direct input from both the non -point and point sources (Table 6). The
load due to non -point sources was almost three times (76%) higher than that of point sources
(24%). Among the point sources, the load due to the Durham Triangle WWTP discharge
was 1.95E+10 colonies per day (0.53%), whereas the load due to the MS4 areas was
8.59E+11 colonies per day (23%).
Among the non -point sources, areas of high intensity development appeared to contribute
high loads to Northeast Creek (60%). High intensity development includes lands where
more than 80% of lands are covered by synthetic coverage. Any coverage between 50% and
80% is considered as low intensity development. The loads due to low intensity
development were comparatively low (12%).
23

Northeast Creek Fecal Coliform TMDL
Urban development, animal grazing, and septic system contribute relatively higher fecal
coliform loads. In urban areas, fecal coliform can be contributed to all creeks by dogs, cats,
raccoons, stormwater runoff, and human waste during storm events. The DWQ staff
hypothesizes that the bacterial load due to the domestic pets accounts for about 10 percent in
the watershed. However, a study to track bacterial sources is required to quantify the actual
sources.
The relative contribution due to wildlife, livestock, and other sources (e.g., wetland and
water pond) was relatively low (❑1%).
Table 6. Total load of fecal coliform (colonies per day) in the Northeast Creek watershed at
SR1100 during the study period, 1997 through 2001.
Source Category
Simulated total
Load
Percent of fecal
coliform load
A. Non -point Sources (LA):
Forest
2.04E+10
0.56
Water body
5.53E+07
0.002
Herbaceous Lands
1.26E+11
3
Urban Development (without MS4)
❑ High intensity development
2.20E+12
60
❑ Low intensity development
4.53E+11
12
B. Point Source (WLA)
MS4 area (Storm water runoff)
8.59E+11
23
Durham Triangle WWTP
1.95E+10
0.53
C. Total for non -point sources
2.80E+12
76
D. Total for point source
8.78E+11
24
E. Grand Total
3.68E+12
100
3.5.2 Critical Period
The critical period is the period when the geometric mean of fecal coliform concentration
reaches peak levels, exceeding the water quality standard of 200 colonies / 100 ml. Fecal
coliform pollution in Northeast Creek watershed originated from both point and non -point
24

Northeast Creek Fecal Coliform TMDL
sources. Usually, excessive concentrations during the dry weather periods are due to point
sources, while excessive concentration during the wet weather periods are due to non -point
M61"iK13
Extreme flows might carry excessive amount of fecal colifrom from both point and non -
point sources to the Northeast Creek. In this study, the extreme flows were defined as the
flows that were exceeded less than 10 percent of the time (90th percentile) during the five
years simulation period. These flows were considered anomalous and were excluded to
estimate the critical period.
Extreme flows were determined by plotting flow duration curve (Figure 9). The duration
curve represents the flow data from October 1982 through September 2002. The duration
curve suggests that the flow that was equal to or above 56 cfs occurred less than 10 percent
of time in the Northeast Creek. The flows below 56 cfs were hence considered for
estimating critical period.
10000
1000
Llowgh
N
100
p
56
10
1
0%
10%
20%
30% 40% 50% 60% 70% 80%
90% 100%
Percent flow exceeded
Transi
tional
Flows
Typical
Flows
Low
Flow
Figure 9. Flow duration curve for Northeast Creek watershed at the ambient station SR
1100 (B3660000).
25

Northeast Creek Fecal Coliform TMDL
The highest 30-day geometric mean of the predicted daily fecal coliform concentration
occurred during wet weather on January 27, 2000 and May 24, 2000 (Appendix 7).
The respective fecal coliform concentration was 503 colonies per 100 ml and 491 colonies
per 100 ml. The difference between the two concentrations was only 12 colonies per 100
ml, which is indeed very close. The result suggests that wet weather is the critical period for
all the seasons in the Northeast Creek watershed.
4.0 ALLOCATION
4.1. Total Maximum Daily Load.
Total Maximum Daily Load (TMDL) can be defined as the total amount of pollutant that
can be assimilated by the receiving water body while achieving water quality standards. A
TMDL can be expressed as the sum of all point source loads (WLAs), non -point source
loads (LAs), and an appropriate margin of safety (MOS), which takes into account any
uncertainty concerning the relationship between effluent limitations and water quality. This
definition can be expressed by equation 5:
TMDL = ❑WLAs + ❑LAs + MOS---------------(5)
The objective of the TMDL is to estimate allowable pollutant loads and to allocate to the
known pollutant sources in the watershed so the appropriate control measures can be
implemented and the water quality standard can be achieved. The Code of Federal
Regulations (40 CFR § 130.2 (1)) states that TMDLs can be expressed in terms of mass per
time, toxicity, or other appropriate measures. For fecal coliform bacteria, TMDLs are
expressed as colonies per 30 days. Therefore, the TMDL represents the maximum fecal
coliform load that can be assimilated by the stream during the critical 30-day period while
maintaining the fecal coliform water quality standard of the geometric mean of 200 colonies
/100 ml over 30 days.
The TMDL was allocated for the ambient station at SR1100 in order to facilitate monitoring
of water quality after the TMDL implementation in future. There was a strong relationship
between the ambient station and the watershed outlet (Figure 10) based on the modeling
26

Northeast Creek Fecal Coliform TMDL
results. The predicted fecal coliform concentration at the outlet of the watershed can be
determined by using the following linear equation 6:
300
250
200
150
100
50
0
y = 0.5031 x - 1.555
R2 = 0.9919
t
0 100 200 300 400 500 600
Geometric mean concentration at Ambient Station
Figure 10. Relationship between the watershed outlet and the ambient station (B3660000)
with regards to the simulated fecal coliform concentrations.
Concentration at outlet = 0.5031 * Concentration at ambient station — 1.555------------(6)
The coefficient of determination (R-Square) was found to be 0.99 for Equation 6. The result
suggests that the variation of the fecal coliform concentration in the watershed outlet is
significantly affected by the variation of the ambient station. The result also suggests that
the variation due to the fecal coliform concentration from the sub -watersheds (WS3 through
WS6) below the station was significantly low.
The TMDL was determined by systematically reducing the watershed loads until all 30-day
geometrical mean concentrations were below the TMDL target of 175 colonies / 100 ml
(marginal of safety = 25 colonies / 100ml). The resulting reduction is presented in Figure 11
for the study period, 1997 through 2001. During the entire study period, the reduction
27

Northeast Creek Fecal Colifonn TMDL
remained below or equal to TMDL target of 175 colonies / 100 ml. None of the fecal
coliform concentration in the same study period exceeded 400 colonies / 100 ml.
1000.00
E
0
0 100.00
it
E
L
0
4-
0
U
10.00
U
d
LL
1.00
ti ti CO 00
Q1 Q1 Q1 �
01 O
01 01
O r
O O
r N N
O O O
r- LO r
\ N r O
O t0
N O
M M
N O
CO M r
N r O
M M V r
O O O r
N
O r
r
O O
ti N T
O O O
Date
• Existing
—Allocation
standard
—MOS
Figure 11. 30-day rolling geometric mean of the simulated fecal colifrom concentration
before and after TMDL allocation at the ambient station (B3660000).
The TMDL for both point source and non -point source was estimated by multiplying the 30-
day geometric mean simulated by the model after reduction by the respective flow values.
The TMDL was then proportionally distributed to each of the sources. The estimation was
done for the period when the maximum 30-day geometric mean was simulated. The existing
average daily load of fecal coliform bacteria at the ambient station is 3.67E+12 colonies /
day (Table 8). The TMDL load at the same location is 3.52E+11 colonies/day.
4.2 Seasonal Variation.
Seasonal variation was incorporated in the continuous simulation of the CRAP model by
using varying loading rates for wet and dry weather periods under varying daily flow
conditions for 5 years, 1997 through 2001. The variation of the predicted and observed fecal

Northeast Creek Fecal Coliform TMDL
coliform bacteria was remained high during both wet and dry weather periods. The
concentration level remained greater than the water quality standard (200 colonies / 100 ml)
for about 70% of the simulation period (Figure 11).
4.3 Margin of Safety (MOS).
The MOS was explicitly included in the TMDL analysis by setting the TMDL target at 175
colonies / 100 ml, which is 25 colonies / 100 ml lower than the water quality target of 200
colonies / 100 ml. Conceptually, the MOS was included in the TMDL estimation to account
for the uncertainty in the simulated relationship between the fecal coliform load and the
water quality standard.
The explicit MOS for this study is, therefore, set to 25 colonies / 100 ml. The daily MOS
load is estimated to be 5.06E+10 colonies. The estimation was performed by calculating the
differences between TMDL with MOS and TMDL without MOS using the equation 2.
4.4. Waste Load Allocation.
The fecal coliform loads in the Northeast Creek watershed due to point sources were about
24% of the total load (Table 6). This percentage of fecal coliform bacteria was attributed to
the two main sources, the Durham Triangle WWTP and the MS4 areas. Both sources
respectively contributed daily fecal coliform load about 1.95E+10 colonies and 8.59E+11
colonies in the ambient site.
The Durham Triangle WWTP was permitted to discharge a monthly geometric mean fecal
coliform concentration of 200 colonies / 100 ml with a maximum permitted discharge of 6
MGD. The total permitted load of fecal coliform bacteria is thus estimated to be 4.54E+10
colonies per day, which is indeed substantially higher than the actual discharge load,
1.95E+10 colonies per day (Table 6). Therefore, a waste load allocation (WLA) reduction
was not recommended for the Durham Triangle WWTP.
However, about 92% of the existing load (8.59E+11 colonies per day) from the MS4 areas
should be reduced. The estimated TMDL for the MS4 areas are about 6.68E+10 (Table 8).
29

Northeast Creek Fecal Coliform TMDL
4.5 Load Allocation (Non -point Source).
The fecal coliform load in Northeast Creek watershed due to non -point sources was about
76% of the total load (Table 6). The model estimation suggests that the TMDL for the non -
point sources be 2.40E+11 colonies per day. On average, the total reduction required to
meet the water quality standard, 175 colonies per 100 ml, is thus estimated to be 91 %
(Table 8).
Table 8. Proposed in -stream fecal coliform load reductions for the Northeast Creek
watershed at SR1008.
Source Category
Simulated total
Load
(Colonies per
day)
TMDL
(Colonies per
day)
Reduction
(%)
A. Non -point Sources (LA):
Forest
2.04E+10
2.04E+10
0
Water body
5.53E+07
5.53E+07
0
Herbaceous Lands
1.26E+11
1.20E+10
90
Urban Development (without MS4)
❑ High intensity development
2.20E+12
1.80E+11
92
❑ Low intensity development
4.53E+11
2.79E+10
94
B. Point Source (WLA)
MS4 area
8.59E+11
6.68E+10
92
Durham Triangle WWTP
1.95E+10
4.54E+10
0
B. Total for non -point sources
2.80E+12
2.40E+11
92
C. Total for point source
8.78E+11
1.12E+11
86
E. Margin of safety (MOS)
5.06E+10
The load allocation distribution for the non -point source was mainly targeted to urban
developed areas, because developed areas contributed substantial fecal coliform bacteria to
Northeast Creek. Fecal coliform bacteria from developed areas can originate from various
sources including leaking sanitary sewers, illicit sanitary sewer connections, and storm water
runoff. Storm water runoff can include waste from domestic animals and urban wildlife.
30

Northeast Creek Fecal Coliform TMDL
Furthermore, the model results suggest that a substantial amount of fecal coliform bacteria
were transported to Northeast Creek from the developed areas in the City of Durham
(outside of the MS4 area) and Research Triangle Park. The total contribution of fecal
coliform bacteria is estimated to be 2.65E+12 colonies per day. About 92-94% of the load
needs to be reduced to meet the water quality standard (Table 8).
Similarly, about 90% of the loads (1.26E+11 colonies) from the herbaceous lands need to be
reduced to meet the water quality standard. Domestic animals and wildlife were seen to be
the main sources of fecal coliform from these lands. Fecal coliform loads from the forested
lands are considered as background sources in this study and hence, the reduction is not
recommended.
Overall, the total fecal coliform load observed in the ambient station, B3660000, was
3.68E+12 colonies per day during the study periods, 1997 through 2001. The estimated
TMDL required to meet the water quality standard, 175 colonies per 100ml of water, at the
station was 4.03E+I I colonies per day. The detailed estimated proportional reductions
required for the various sources in the Northeast Creek watershed are presented in Table 8.
5.0 SUMMARY AND FUTURE CONSIDERATIONS
The CRAP model estimated that the non -point sources contributed 76% of the total load
(3.68E+12 colonies per day) in the Northeast Creek. The contribution was primarily due to
urban development. In order for the water quality target to be met, the final allocation of the
fecal coliform bacteria requires a reduction of 2.40E+11 colonies per day for the various
non -point sources.
The pipelines connecting between the Durham Triangle WWTP and the sewage collection
system in the watershed run along the main Northeast Creek. Failure of connection between
the sewer pipelines or any leak from the pipe could result in profound fecal coliform loads in
31

Northeast Creek Fecal Coliform TMDL
the creek. The city of Durham and the respected line agencies are therefore suggested to
check any leak from the connecting pipe.
The model estimated that the point sources contributed about 24% of the total loading in the
watershed. A majority of that load was contributed by storm water runoff from the City of
Durham MS4 area. About 92% of the load (8.59E+11 colonies per day) was estimated to be
reduced to meet the water quality. In contrast, the reduction is not recommended for fecal
coliform loading from the WWTP. The waste load allocation for the WWTP, in accordance
with the NPDES permit, was estimated to be 4.54E+10 colonies per day. The permitted load
appeared to be marginally higher than the actual discharged load, 1.95E+10 colonies per
day.
5.1 Monitoring
Fecal coliform monitoring will continue on a monthly interval at the existing ambient
monitoring site. The continued monitoring of fecal coliform concentrations will allow for
the evaluation of progress towards the goal of reaching water quality standards by
comparing the instream data to the TMDL target.
To comply with EPA guidance, North Carolina may adopt new bacteria standards utilizing
Escherichia coli (E. coli) or enterococci in the near future. Thus, in future, monitoring
efforts to measure compliance with this TMDL should include using E. coli or enterococci.
Per EPA recommendations (EPA, 2000b), if future monitoring for E. coli/enterococci
indicates the standard has not been exceeded, these monitoring data may be used to support
delisting the water body from the 303(d) list. If a continuing problem is identified using E.
coli/enterococci, the TMDL may be revised.
5.2 Implementation
Implementation plans are not included in this TMDL. The involvement of local
governments and agencies will be needed in order to develop implementation plans. The
DWQ will initiate the development of an implementation plan.
32

Northeast Creek Fecal Coliform TMDL
6.0 PUBLIC PARTICIPATION
Many local government officials have been notified of DWQ's intention to develop the
Northeast Creek fecal coliform TMDL. The extension services in Durham County,
Chatham County, Wake County and local associations have supplied septic data, sewer data,
agricultural information, and stormwater runoff in MS4 areas to aid in the source assessment
portion of the TMDL. The Northeast Creek Fecal Colifom TMDL was public noticed
through local newspapers, The Herald -Sun and The Chatham Record, on May 6 and May 8,
2003 respectively (Appendix 8). The TMDL was also public noticed through DWQ web site
at httD://h20.enr.state.nc.us/tmdl/.
A public meeting was held in Durham County Agricultural Building and Curb Market, NC,
on May 27, 2003 as a part of the comment period. A group of eight (8) individuals
participated the meeting from the following organizations:
City of Durham, Stormwater Services — 5 representatives
Cooperative Extension Service — 1 representative
Raleigh Regional Office — 2 representatives
A public comment period was through June 5, 2003. No written comments were received.
33

Northeast Creek Fecal Coliform TMDL
7.0 REFERENCES
Center for Watershed Protection. 1999. Microbes and Urban Watershed: Concentrations,
Sources, and Pathways. Watershed Protection Techniques 3(1): 554:565.
Clark, Melanie L. Clark and Jodi R. Norris. 2000. Occurance of Fecal Coliform Bacteria in
Selected Streams in Wyoming, 1990-99. Water Resources Investigations Report 00-4198.
USGS, Science for a Changing World. Cheyenne, Wyoming.
Canale, R. P., M.T. Auer, E.M. Owens, T.M. Heidtke, S.W. Effler. 1993. Modeling Fecal
Coliform Bacteria —II. Model Development and Application. Water Research, 27(4):703-
714.
Division of Environmental Health (DEH). NCDENR. 2000. Report on the Proper
Maintenance of Septic Tank Systems in Accordance with Section 13.5 of HB 1160 (Clean
Water Act of 1999). http://www.deh.enr.state.nc.us/oww/Maintenance.PDF. March 15,
2000.
Doran, J.W., J.S. Schepers, and N.P. Swanson. 1981. Chemical and Biological Quality of
Pasture Runoff. Journal of Soil and Water Conservation. May -June: 166-171.
Farrell -Poe, K.L., Ranjha, A.Y. and S. Ramalingam. 1997. Bacterial Contribution by Rural
Municipalities in Agricultural Watersheds. Trans of ASAE, 40(1) 97-101.
Hyer, Kenneth, Doughlas Moyer, and Trisha Baldwin. 2001. Bacteria Source Tracking to
Improve TMDL Development in Bacteria. U.S. Geological Survey, WRD, 1730 East
Parham Rd., Richmond, VA 23228. In va.water.usgs.gov/GLOBAL/posters/BST.pdf.
Khaleel, R., K.R. Reddy, and M.R. Overcash. 1980. Transport of Potential Pollutants in
Runoff Water from Land Areas Receiving Animal Wastes: A Review. Water Research
14:421-436.
Marsalek, J. 2002. Urban Wet -Weather Flows: Sources of Fecal Coliform Loads Impacting
on Recreational Waters and Threatening Drinking Water Resources.
hit2://www.neram.ca/Pages/events/abstracts/marsalek.pdf
North Carolina Department of Environment and Natural Resources, Division of Water
Quality. 2002. North Carolina's 2003 § 303(d) List.
http://h2o.enr.state.nc.us/tmdl/General-303d.htm
U.S. Environmental Protection Agency (USEPA). 1991. Guidance for Water Quality -Based
Decisions: The TMDL Process. Assessment and Watershed Protection Division,
Washington, DC.
U.S. Environmental Protection Agency, Federal Advisory Committee (FACA). Draft final
TMDL Federal Advisory Committee Report. 4/28/98.
34

Northeast Creek Fecal Coliform TMDL
U.S. Environmental Protection Agency (USEPA) 2000a. Revisions to the Water Quality
Planning and Management Regulation and Revisions to the National Pollutant Discharge
Elimination System Program in Support of Revisions to the Water Quality Planning and
management Regulation; Final Rule. Fed. Reg. 65:43586-43670 (July 13, 2000).
U.S.Environmental Protection Agency (USEPA) 2000b. Implementation Guidance for
Ambient Water Quality Criteria for Bacteria — 1986. DRAFT. Office of Water. EPA-823-
D-00-001.
U.S.Environmental Protection Agency (USEPA). January 2000. Storm Water Phase H Final
Rule. Small MS4 Storm Water Program Overview. EPA 833-F-00-002. Fact Sheet 2.0.
U.S.Environmental Protection Agency (USEPA). January 2001. Protocal for Developing
Pathogen TMDLs: First Edition. http://www.epa.gov/owow/tmdl/techsupp.html.
U.S.Environmental Protection Agency (USEPA). February 2002. TMDLs for Fecal
Coliform in 303(d) Listed Streams in Altamaha River Basin.
http://epa.gov/region4/water/tmdl/georgia.
U.S. Environmental Protection Agency (USEPA) 2002. Establishing Total Maximum Daily
Load (TMDL) Watershed Allocations (WLAs) for Storm Water Sources and NPDES Permit
Requirements Based on this WLAs. Guidance memrandum from Robert Wayland,III and
James Hanlon. November 22, 2002.
U.S. Environmental Protection Agency (USEPA) 1985. Rates, constants, and kinetics
formulations in surface water quality modeling (II ed.). Athens, GA: EPA-600-3-85-040.
Weaver, J. Curtis and Benjamin F. Pope. 2001. Low -Flow Characteristics and Discharge
Profiles for Selected Streams in the Cape Fear River Basin, North Carolina, through 1998.
U.S.G.S. Water -Resources Investigations Report 01-4094.
Wilhelm, Lance J. and Terry L. Maluk. October 1998. Fecal -Indicator Bacteria in Surface
Waters of the Santee River Basin and Coastal Drainages, North and South Carolina, 1995-
98. Fact Sheet FS-085-98. U.S. Geological Survey, Columbia, SC 29210-7651.
35

Northeast Creek Fecal Coliform TMDL
Appendix 1. Fecal Coliform in the Ambient Station (133660000)
Appendix 1.1 Table of fecal coliform responses during 1997 through 2001.
Date Weather
Fecal
Flow
Date Weather
Fecal Flow
Status
(col/100
(cfs)
Status
(col/100 (cfs)
MI)
MI)
1 /15/97 dry
63
18
1 /13/00 wet
490
32
2/3/97 dry
1000
19
2/22/00 dry
4500
27
3/21 /97 wet
3
67
3/28/00 wet
1400
27
4/11/97 dry
2
6.9
4/18/00 wet
2700
154
5/13/97 dry
2000
7.2
6/1/00 dry
136
9.2
7/2/97 dry
100
8.9
6/28/00 wet
650
9.9
8/25/97 dry
0.2
5.8
7/31/00 wet
3200
14
9/10/97 wet
18
14
8/30/00 wet
540
29
10/20/97 wet
7.9
35
9/25/00 wet
230
14
11/17/97 dry
12
10
10/10/00 dry
210
5.2
12/11 /97 wet
95
28
11 /29/00 dry
200
5.5
1 / 12/98 dry
73
12
12/27/00 dry
170
19
2/10/98 dry
210
15
2/1/01 wet
67
20
3/3/98 dry
11000
10
4/ 19/01 d ry
360
6.7
4/15/98 wet
91
16
5/9/01 dry
200
5
5/26/98 wet
540
7.4
6/28/01 d ry
130
8.5
6/11/98 dry
560
7.4
7/26/01 wet
6000
18
7/29/98 wet
770
7.7
8/15/01 dry
260
18
8/31 /98 wet
1200
6.3
10/4/01 d ry
280
6.5
9/28/98 dry
260
4
11 /5/01 d ry
72
7.2
10/27/98 dry
470
6.8
11 /29/01 d ry
420
4.2
11 /29/98 dry
62
4.3
12/29/98 dry
110
5
1/27/99 dry
100
23
2/17/99 dry
2200
7.8
3/18/99 dry
170
17
4/29/99 wet
2000
23
5/24/99 dry
270
4.3
6/24/99 dry
290
3.9
7/28/99 dry
760
3.5
8/18/99 dry
350
4
9/28/99 wet
4200
528
11 /1 /99 wet
410
11
11 /3/99 wet
330
18
11 /6/99 wet
71
10
11/15/99 dry
100
8.7
11 /29/99 wet
410
5.2
12/ 1 /99 dry
580
3.7
36

Northeast Creek Fecal Coliform TMDL
Appendix 1.2. Graphical responses of fecal coliform
Concentration of Fecal Coliform at B3660000
(1997)
^ 3000 80
N
R o 0 2000 60
0 40 3
0 1000 20 _o
v" 0 0 LL
01 02 03 04 05 06 07 08 09 10 11 12
Months
Flow (cfs) —Observed —Standard
Concentration of Fecal Coliform at B3660000
(1998)
12000 20
" 10000
m 0 8000 15 U
° 6000 10 3
LL O O
4000 0
V 2000 5 LL
0 0 L, 0
01 02 03 04 05 06 07 08 09 10 11 12
Months
Flow (cfs) —Observed —Standard
Concentration of Fecal Coliform at B3660000
(1999)
5000 600
£ 4000 500 y
CD3000 400
LL .o = 2000 300 3
200 0
v V 1000 100 LL
0 L 0
01 02 03 04 05 06 07 08 09 11 11 11 11 11 12
Months
Flow (cfs) —Observed — Standard
37

Northeast Creek Fecal Coliform TMDL
Appendix 1.2 continued.
Concentration of Fecal Coliform at B3660000
(2000)
5000 200
£ £ 4000 150 w
c 3000
0 = = 2000 100 3
V u 1000 50 LL0
0 0
01 02 03 04 06 06 07 08 09 10 11 12
Months
Flow (cfs) —Observed —Standard
Concentration of Fecal Coliform at B3660000
(2001)
8000
25
£ £ 6000
20 H
p o
15
c 4000
LL
v i 20000
�
n
10 c
5
02 04 05 06 07 08 10 11 11
Months
Flow (cfs) —Observed —Standard

Northeast Creek Fecal Coliform TMDL
Appendix 2. Flow Recorded by USGS at the ambient Station (133660000).
Date
Flow
Date
Flow
Date Flow
Date
Flow Date
Flow
(cfs)
(cfs)
(cfs)
(cfs)
(cfs)
01 /01 /97
20.00
01 /01 /98
11.00
01 /01 /99
3.90
01 /01 /00
28.00
01 /01 /01
18.00
01 /02/97
25.00
01 /02/98
9.00
01 /02/99
3.60
01 /02/00
27.00
01 /02/01
18.00
01 /03/97
21.00
01 /03/98
8.10
01 /03/99
518.00
01 /03/00
28.00
01 /03/01
18.00
01 /04/97
18.00
01 /04/98
7.20
01 /04/99
303.00
01 /04/00
31.00
01 /04/01
19.00
01 /05/97
17.00
01 /05/98
7.40
01 /05/99
36.00
01 /05/00
57.00
01 /05/01
19.00
01 /06/97
18.00
01 /06/98
7.50
01 /06/99
18.00
01 /06/00
32.00
01 /06/01
18.00
01 /07/97
15.00
01 /07/98
10.00
01 /07/99
14.00
01 /07/00
29.00
01 /07/01
19.00
01 /08/97
14.00
01 /08/98
197.00
01 /08/99
12.00
01 /08/00
28.00
01 /08/01
21.00
01 /09/97
165.00
01 /09/98
312.00
01 /09/99
11.00
01 /09/00
32.00
01 /09/01
22.00
01/10/97
334.00
01/10/98
43.00
01/10/99
10.00
01/10/00
207.00
01/10/01
22.00
01/11/97
82.00
01/11/98
17.00
01/11/99
9.60
01/11/00
278.00
01/11/01
21.00
01/12/97
30.00
01/12/98
12.00
01/12/99
9.20
01/12/00
48.00
01/12/01
22.00
01/13/97
23.00
01/13/98
11.00
01/13/99
9.10
01/13/00
32.00
01/13/01
21.00
01/14/97
19.00
01/14/98
11.00
01/14/99
8.30
01/14/00
28.00
01/14/01
22.00
01/15/97
18.00
01/15/98
40.00
01/15/99
25.00
01/15/00
25.00
01/15/01
23.00
01/16/97
139.00
01/16/98
362.00
01/16/99
20.00
01/16/00
24.00
01/16/01
23.00
01/17/97
182.00
01/17/98
616.00
01/17/99
11.00
01/17/00
25.00
01/17/01
22.00
01/18/97
36.00
01/18/98
135.00
01/18/99
178.00
01/18/00
25.00
01/18/01
23.00
01/19/97
22.00
01/19/98
107.00
01/19/99
194.00
01/19/00
28.00
01/19/01
23.00
01 /20/97
21.00
01 /20/98
259.00
01 /20/99
29.00
01 /20/00
43.00
01 /20/01
50.00
01 /21 /97
19.00
01 /21 /98
69.00
01 /21 /99
17.00
01 /21 /00
57.00
01 /21 /01
34.00
01 /22/97
17.00
01 /22/98
24.00
01 /22/99
13.00
01 /22/00
32.00
01 /22/01
23.00
01 /23/97
18.00
01 /23/98
192.00
01 /23/99
14.00
01 /23/00
36.00
01 /23/01
20.00
01 /24/97
19.00
01 /24/98
374.00
01 /24/99
548.00
01 /24/00
53.00
01 /24/01
19.00
01 /25/97
75.00
01 /25/98
116.00
01 /25/99
394.00
01 /25/00
65.00
01 /25/01
18.00
01 /26/97
74.00
01 /26/98
28.00
01 /26/99
66.00
01 /26/00
53.00
01 /26/01
17.00
01 /27/97
28.00
01 /27/98
95.00
01 /27/99
23.00
01 /27/00
39.00
01 /27/01
16.00
01 /28/97
49.00
01 /28/98
767.00
01 /28/99
17.00
01 /28/00
33.00
01 /28/01
16.00
01 /29/97
90.00
01 /29/98
239.00
01 /29/99
14.00
01 /29/00
20.00
01 /29/01
18.00
01 /30/97
35.00
01 /30/98
52.00
01 /30/99
11.00
01 /30/00
108.00
01 /30/01
21.00
01 /31 /97
39.00
01 /31 /98
22.00
01 /31 /99
9.40
01 /31 /00
579.00
01 /31 /01
22.00
02/01 /97
29.00
02/01 /98
16.00
02/01 /99
12.00
02/01 /00
224.00
02/01 /01
20.00
02/02/97
22.00
02/02/98
14.00
02/02/99
102.00
02/02/00
101.00
02/02/01
19.00
02/03/97
19.00
02/03/98
15.00
02/03/99
66.00
02/03/00
67.00
02/03/01
17.00
02/04/97
18.00
02/04/98
623.00
02/04/99
23.00
02/04/00
99.00
02/04/01
17.00
02/05/97
17.00
02/05/98
449.00
02/05/99
19.00
02/05/00
101.00
02/05/01
21.00
02/06/97
17.00
02/06/98
170.00
02/06/99
13.00
02/06/00
57.00
02/06/01
21.00
02/07/97
15.00
02/07/98
41.00
02/07/99
12.00
02/07/00
44.00
02/07/01
19.00
02/08/97
35.00
02/08/98
26.00
02/08/99
11.00
02/08/00
39.00
02/08/01
18.00
02/09/97
55.00
02/09/98
19.00
02/09/99
9.90
02/09/00
35.00
02/09/01
17.00
02/10/97
27.00
02/10/98
15.00
02/10/99
9.10
02/10/00
32.00
02/10/01
16.00
02/11/97
23.00
02/11/98
13.00
02/11/99
8.70
02/11/00
31.00
02/11/01
16.00
02/12/97
19.00
02/12/98
15.00
02/12/99
8.50
02/12/00
68.00
02/12/01
15.00
02/13/97
17.00
02/13/98
13.00
02/13/99
8.10
02/13/00
181.00
02/13/01
25.00
02/14/97
328.00
02/14/98
10.00
02/14/99
7.40
02/14/00
110.00
02/14/01
40.00
02/15/97
438.00
02/15/98
9.30
02/15/99
7.60
02/15/00
100.00
02/15/01
36.00
02/16/97
245.00
02/16/98
18.00
02/16/99
7.80
02/16/00
37.00
02/16/01
30.00
39

Northeast Creek Fecal Coliform TMDL
Appendix 2 continued
02/17/97
52.00
02/17/98
841.00
02/17/99
7.80
02/17/00
31.00
02/17/01
400.00
02/18/97
29.00
02/18/98
427.00
02/18/99
29.00
02/18/00
86.00
02/18/01
120.00
02/19/97
25.00
02/19/98
74.00
02/19/99
28.00
02/19/00
79.00
02/19/01
60.00
02/20/97
21.00
02/20/98
28.00
02/20/99
100.00
02/20/00
38.00
02/20/01
35.00
02/21 /97
19.00
02/21 /98
19.00
02/21 /99
31.00
02/21 /00
30.00
02/21 /01
21.00
02/22/97
22.00
02/22/98
13.00
02/22/99
16.00
02/22/00
27.00
02/22/01
19.00
02/23/97
17.00
02/23/98
73.00
02/23/99
12.00
02/23/00
25.00
02/23/01
17.00
02/24/97
17.00
02/24/98
106.00
02/24/99
10.00
02/24/00
25.00
02/24/01
18.00
02/25/97
14.00
02/25/98
25.00
02/25/99
9.60
02/25/00
24.00
02/25/01
19.00
02/26/97
13.00
02/26/98
16.00
02/26/99
9.10
02/26/00
23.00
02/26/01
20.00
02/27/97
14.00
02/27/98
13.00
02/27/99
8.20
02/27/00
27.00
02/27/01
17.00
02/28/97
16.00
02/28/98
12.00
02/28/99
8.20
02/28/00
215.00
02/28/01
15.00
03/01 /97
25.00
03/01 /98
11.00
03/01 /99
10.00
02/29/00
50.00
03/01 /01
14.00
03/02/97
18.00
03/02/98
11.00
03/02/99
9.30
03/01 /00
16.00
03/02/01
13.00
03/03/97
20.00
03/03/98
10.00
03/03/99
8.50
03/02/00
13.00
03/03/01
20.00
03/04/97
30.00
03/04/98
9.50
03/04/99
8.90
03/03/00
12.00
03/04/01
200.00
03/05/97
20.00
03/05/98
8.90
03/05/99
8.30
03/04/00
11.00
03/05/01
130.00
03/06/97
38.00
03/06/98
8.30
03/06/99
7.10
03/05/00
10.00
03/06/01
80.00
03/07/97
21.00
03/07/98
7.30
03/07/99
6.50
03/06/00
10.00
03/07/01
48.00
03/08/97
14.00
03/08/98
99.00
03/08/99
7.40
03/07/00
9.60
03/08/01
30.00
03/09/97
12.00
03/09/98
545.00
03/09/99
7.80
03/08/00
9.50
03/09/01
25.00
03/10/97
13.00
03/10/98
242.00
03/10/99
9.70
03/09/00
9.40
03/10/01
20.00
03/11/97
12.00
03/11/98
36.00
03/11/99
9.40
03/10/00
9.30
03/11/01
16.00
03/12/97
11.00
03/12/98
20.00
03/12/99
8.60
03/11/00
8.40
03/12/01
14.00
03/13/97
12.00
03/13/98
14.00
03/13/99
7.60
03/12/00
8.50
03/13/01
14.00
03/14/97
37.00
03/14/98
11.00
03/14/99
20.00
03/13/00
8.70
03/14/01
13.00
03/15/97
61.00
03/15/98
10.00
03/15/99
400.00
03/14/00
8.80
03/15/01
15.00
03/16/97
19.00
03/16/98
9.80
03/16/99
144.00
03/15/00
8.60
03/16/01
16.00
03/17/97
14.00
03/17/98
10.00
03/17/99
27.00
03/16/00
8.80
03/17/01
13.00
03/18/97
13.00
03/18/98
288.00
03/18/99
17.00
03/17/00
12.00
03/18/01
8.00
03/19/97
153.00
03/19/98
1720.00
03/19/99
13.00
03/18/00
8.90
03/19/01
6.00
03/20/97
315.00
03/20/98
319.00
03/20/99
10.00
03/19/00
8.10
03/20/01
9.00
03/21 /97
67.00
03/21 /98
238.00
03/21 /99
123.00
03/20/00
14.00
03/21 /01
459.00
03/22/97
23.00
03/22/98
146.00
03/22/99
349.00
03/21 /00
57.00
03/22/01
280.00
03/23/97
15.00
03/23/98
44.00
03/23/99
61.00
03/22/00
16.00
03/23/01
37.00
03/24/97
13.00
03/24/98
34.00
03/24/99
21.00
03/23/00
12.00
03/24/01
15.00
03/25/97
11.00
03/25/98
21.00
03/25/99
16.00
03/24/00
10.00
03/25/01
11.00
03/26/97
14.00
03/26/98
18.00
03/26/99
20.00
03/25/00
9.50
03/26/01
9.70
03/27/97
12.00
03/27/98
15.00
03/27/99
14.00
03/26/00
9.00
03/27/01
8.80
03/28/97
9.80
03/28/98
13.00
03/28/99
11.00
03/27/00
9.90
03/28/01
8.30
03/29/97
9.90
03/29/98
13.00
03/29/99
10.00
03/28/00
27.00
03/29/01
125.00
03/30/97
9.90
03/30/98
13.00
03/30/99
9.90
03/29/00
13.00
03/30/01
722.00
03/31 /97
9.60
03/31 /98
12.00
03/31 /99
9.00
03/30/00
11.00
03/31 /01
224.00
04/01 /97
9.30
04/01 /98
54.00
04/01 /99
53.00
03/31 /00
9.90
04/01 /01
345.00
04/02/97
8.10
04/02/98
41.00
04/02/99
174.00
04/01 /00
8.60
04/02/01
402.00
04/03/97
7.80
04/03/98
17.00
04/03/99
30.00
04/02/00
9.30
04/03/01
76.00
04/04/97
8.10
04/04/98
34.00
04/04/99
16.00
04/03/00
11.00
04/04/01
30.00
04/05/97
7.20
04/05/98
22.00
04/05/99
14.00
04/04/00
13.00
04/05/01
16.00
04/06/97
7.40
04/06/98
15.00
04/06/99
11.00
04/05/00
12.00
04/06/01
11.00
04/07/97
16.00
04/07/98
13.00
04/07/99
10.00
04/06/00
12.00
04/07/01
10.00
04/08/97
11.00
04/08/98
11.00
04/08/99
9.50
04/07/00
12.00
04/08/01
9.10
IN

Northeast Creek Fecal Coliform TMDL
Appendix 2 continued.
04/09/97
8.00
04/09/98
116.00
04/09/99
9.30
04/08/00
18.00
04/09/01
9.00
04/10/97
7.20
04/10/98
119.00
04/10/99
7.90
04/09/00
51.00
04/10/01
8.40
04/11/97
6.90
04/11/98
24.00
04/11/99
37.00
04/10/00
13.00
04/11/01
8.10
04/12/97
12.00
04/12/98
15.00
04/12/99
69.00
04/11/00
12.00
04/12/01
7.60
04/13/97
19.00
04/13/98
12.00
04/13/99
15.00
04/12/00
9.90
04/13/01
7.30
04/14/97
9.80
04/14/98
13.00
04/14/99
10.00
04/13/00
11.00
04/14/01
6.40
04/15/97
7.90
04/15/98
16.00
04/15/99
9.00
04/14/00
16.00
04/15/01
6.20
04/16/97
7.60
04/16/98
12.00
04/16/99
8.70
04/15/00
36.00
04/16/01
6.50
04/17/97
10.00
04/17/98
25.00
04/17/99
7.50
04/16/00
31.00
04/17/01
6.80
04/18/97
7.30
04/18/98
23.00
04/18/99
7.00
04/17/00
14.00
04/18/01
6.80
04/19/97
6.20
04/19/98
16.00
04/19/99
7.60
04/18/00
154.00
04/19/01
6.70
04/20/97
5.80
04/20/98
18.00
04/20/99
7.90
04/19/00
70.00
04/20/01
6.40
04/21 /97
6.60
04/21 /98
12.00
04/21 /99
7.80
04/20/00
22.00
04/21 /01
5.90
04/22/97
40.00
04/22/98
10.00
04/22/99
7.70
04/21 /00
19.00
04/22/01
6.00
04/23/97
112.00
04/23/98
9.40
04/23/99
7.80
04/22/00
16.00
04/23/01
6.00
04/24/97
82.00
04/24/98
8.70
04/24/99
6.90
04/23/00
15.00
04/24/01
6.00
04/25/97
19.00
04/25/98
7.30
04/25/99
6.40
04/24/00
15.00
04/25/01
9.00
04/26/97
11.00
04/26/98
6.90
04/26/99
7.10
04/25/00
17.00
04/26/01
7.50
04/27/97
7.70
04/27/98
7.40
04/27/99
7.70
04/26/00
19.00
04/27/01
6.00
04/28/97
280.00
04/28/98
8.10
04/28/99
10.00
04/27/00
37.00
04/28/01
5.00
04/29/97
875.00
04/29/98
7.40
04/29/99
23.00
04/28/00
34.00
04/29/01
5.40
04/30/97
249.00
04/30/98
7.00
04/30/99
185.00
04/29/00
58.00
04/30/01
5.60
05/01 /97
57.00
05/01 /98
7.60
05/01 /99
92.00
04/30/00
31.00
05/01 /01
6.00
05/02/97
118.00
05/02/98
9.50
05/02/99
7.50
05/01 /00
18.00
05/02/01
5.90
05/03/97
38.00
05/03/98
6.90
05/03/99
5.10
05/02/00
15.00
05/03/01
5.80
05/04/97
38.00
05/04/98
8.80
05/04/99
4.00
05/03/00
14.00
05/04/01
5.70
05/05/97
16.00
05/05/98
7.50
05/05/99
3.70
05/04/00
14.00
05/05/01
5.50
05/06/97
12.00
05/06/98
6.50
05/06/99
3.80
05/05/00
14.00
05/06/01
5.40
05/07/97
9.80
05/07/98
6.40
05/07/99
4.10
05/06/00
14.00
05/07/01
5.30
05/08/97
8.50
05/08/98
16.00
05/08/99
3.80
05/07/00
15.00
05/08/01
5.00
05/09/97
8.20
05/09/98
9.10
05/09/99
3.40
05/08/00
15.00
05/09/01
5.00
05/10/97
7.00
05/10/98
6.90
05/10/99
3.80
05/09/00
16.00
05/10/01
4.90
05/11/97
6.30
05/11/98
79.00
05/11/99
3.70
05/10/00
16.00
05/11/01
4.80
05/12/97
6.80
05/12/98
34.00
05/12/99
4.00
05/11/00
16.00
05/12/01
4.80
05/13/97
7.20
05/13/98
11.00
05/13/99
4.00
05/12/00
16.00
05/13/01
5.00
05/14/97
7.60
05/14/98
8.00
05/14/99
4.20
05/13/00
16.00
05/14/01
4.60
05/15/97
7.00
05/15/98
6.90
05/15/99
5.30
05/14/00
16.00
05/15/01
4.00
05/16/97
6.40
05/16/98
6.00
05/16/99
4.00
05/15/00
16.00
05/16/01
20.00
05/17/97
5.70
05/17/98
5.70
05/17/99
4.00
05/16/00
17.00
05/17/01
10.00
05/18/97
5.50
05/18/98
6.00
05/18/99
4.30
05/17/00
17.00
05/18/01
5.20
05/19/97
6.30
05/19/98
6.10
05/19/99
4.30
05/18/00
17.00
05/19/01
5.10
05/20/97
6.40
05/20/98
5.90
05/20/99
4.40
05/19/00
16.00
05/20/01
5.00
05/21 /97
6.30
05/21 /98
6.10
05/21 /99
4.30
05/20/00
16.00
05/21 /01
5.00
05/22/97
6.20
05/22/98
5.80
05/22/99
4.70
05/21 /00
16.00
05/22/01
5.50
05/23/97
5.80
05/23/98
16.00
05/23/99
5.90
05/22/00
30.00
05/23/01
6.00
05/24/97
5.30
05/24/98
19.00
05/24/99
4.30
05/23/00
17.00
05/24/01
5.60
05/25/97
6.20
05/25/98
9.80
05/25/99
4.00
05/24/00
12.00
05/25/01
5.30
05/26/97
21.00
05/26/98
7.40
05/26/99
3.90
05/25/00
10.00
05/26/01
42.00
05/27/97
13.00
05/27/98
9.80
05/27/99
3.80
05/26/00
9.60
05/27/01
17.00
05/28/97
7.20
05/28/98
7.60
05/28/99
3.50
05/27/00
8.30
05/28/01
7.00
05/29/97
6.20
05/29/98
7.00
05/29/99
3.00
05/28/00
8.00
05/29/01
6.10
41

Northeast Creek Fecal Coliform TMDL
Appendix 2 continued
05/30/97
6.20
05/30/98
6.10
05/30/99
2.60
05/29/00
11.00
05/30/01
5.60
05/31 /97
5.70
05/31 /98
5.70
05/31 /99
3.00
05/30/00
12.00
05/31 /01
5.00
06/01 /97
8.80
06/01 /98
6.00
06/01 /99
3.50
05/31 /00
10.00
06/01 /01
80.00
06/02/97
21.00
06/02/98
6.00
06/02/99
3.90
06/01 /00
9.20
06/02/01
50.00
06/03/97
26.00
06/03/98
5.70
06/03/99
3.90
06/02/00
9.00
06/03/01
30.00
06/04/97
16.00
06/04/98
28.00
06/04/99
3.80
06/03/00
7.90
06/04/01
18.00
06/05/97
8.80
06/05/98
19.00
06/05/99
3.20
06/04/00
9.40
06/05/01
12.00
06/06/97
8.30
06/06/98
9.40
06/06/99
3.00
06/05/00
9.60
06/06/01
8.50
06/07/97
13.00
06/07/98
10.00
06/07/99
3.70
06/06/00
9.60
06/07/01
6.00
06/08/97
7.30
06/08/98
7.50
06/08/99
3.90
06/07/00
8.60
06/08/01
5.50
06/09/97
6.40
06/09/98
6.40
06/09/99
4.20
06/08/00
8.30
06/09/01
5.00
06/10/97
6.00
06/10/98
7.40
06/10/99
4.50
06/09/00
8.00
06/10/01
4.40
06/11/97
5.80
06/11/98
7.40
06/11/99
4.80
06/10/00
7.10
06/11/01
4.00
06/12/97
6.00
06/12/98
6.60
06/12/99
4.10
06/11/00
7.40
06/12/01
3.50
06/13/97
12.00
06/13/98
5.80
06/13/99
4.30
06/12/00
8.40
06/13/01
6.00
06/14/97
8.30
06/14/98
5.10
06/14/99
5.70
06/13/00
8.40
06/14/01
30.00
06/15/97
5.80
06/15/98
12.00
06/15/99
9.10
06/14/00
8.40
06/15/01
15.00
06/16/97
5.70
06/16/98
13.00
06/16/99
9.30
06/15/00
8.60
06/16/01
6.00
06/17/97
5.90
06/17/98
7.50
06/17/99
32.00
06/16/00
8.50
06/17/01
4.50
06/18/97
5.90
06/18/98
6.20
06/18/99
5.80
06/17/00
7.50
06/18/01
3.30
06/19/97
5.90
06/19/98
5.80
06/19/99
3.80
06/18/00
6.80
06/19/01
2.90
06/20/97
5.60
06/20/98
5.10
06/20/99
3.20
06/19/00
8.10
06/20/01
2.40
06/21 /97
4.90
06/21 /98
4.80
06/21 /99
3.40
06/20/00
8.80
06/21 /01
2.20
06/22/97
4.60
06/22/98
5.50
06/22/99
3.80
06/21 /00
8.50
06/22/01
3.80
06/23/97
5.30
06/23/98
5.70
06/23/99
3.90
06/22/00
8.90
06/23/01
6.00
06/24/97
5.50
06/24/98
6.10
06/24/99
3.90
06/23/00
8.30
06/24/01
5.20
06/25/97
5.70
06/25/98
5.90
06/25/99
4.10
06/24/00
7.40
06/25/01
40.00
06/26/97
5.80
06/26/98
5.80
06/26/99
4.00
06/25/00
6.80
06/26/01
19.00
06/27/97
7.80
06/27/98
5.10
06/27/99
4.50
06/26/00
7.70
06/27/01
10.00
06/28/97
6.30
06/28/98
4.80
06/28/99
4.70
06/27/00
8.50
06/28/01
8.50
06/29/97
5.10
06/29/98
5.30
06/29/99
4.90
06/28/00
9.90
06/29/01
7.00
06/30/97
5.60
06/30/98
6.00
06/30/99
4.60
06/29/00
15.00
06/30/01
6.00
07/01 /97
6.20
07/01 /98
8.10
07/01 /99
4.70
06/30/00
9.70
07/01 /01
5.00
07/02/97
8.90
07/02/98
5.90
07/02/99
5.00
07/01 /00
6.70
07/02/01
4.90
07/03/97
6.50
07/03/98
4.80
07/03/99
4.30
07/02/00
5.80
07/03/01
4.80
07/04/97
5.20
07/04/98
4.60
07/04/99
3.70
07/03/00
5.70
07/04/01
5.00
07/05/97
7.50
07/05/98
19.00
07/05/99
3.50
07/04/00
6.40
07/05/01
5.00
07/06/97
5.70
07/06/98
8.30
07/06/99
4.00
07/05/00
8.10
07/06/01
4.90
07/07/97
5.60
07/07/98
6.20
07/07/99
4.10
07/06/00
10.00
07/07/01
4.80
07/08/97
5.40
07/08/98
5.60
07/08/99
4.10
07/07/00
12.00
07/08/01
7.00
07/09/97
5.50
07/09/98
9.00
07/09/99
4.10
07/08/00
11.00
07/09/01
7.80
07/10/97
5.60
07/10/98
6.90
07/10/99
4.20
07/09/00
12.00
07/10/01
8.00
07/11/97
5.40
07/11/98
5.50
07/11/99
4.70
07/10/00
14.00
07/11/01
6.20
07/12/97
4.50
07/12/98
4.70
07/12/99
5.30
07/11/00
15.00
07/12/01
5.00
07/13/97
4.40
07/13/98
5.10
07/13/99
8.00
07/12/00
15.00
07/13/01
5.00
07/14/97
5.20
07/14/98
5.40
07/14/99
25.00
07/13/00
16.00
07/14/01
4.90
07/15/97
5.50
07/15/98
5.60
07/15/99
9.10
07/14/00
15.00
07/15/01
4.80
07/16/97
6.10
07/16/98
14.00
07/16/99
5.40
07/15/00
20.00
07/16/01
4.70
07/17/97
11.00
07/17/98
31.00
07/17/99
3.70
07/16/00
16.00
07/17/01
4.50
07/18/97
6.90
07/18/98
19.00
07/18/99
3.20
07/17/00
13.00
07/18/01
4.40
07/19/97
5.30
07/19/98
6.80
07/19/99
3.60
07/18/00
13.00
07/19/01
4.30
42

Northeast Creek Fecal Coliform TMDL
Appendix 2 Continued
07/20/97
4.80
07/20/98
6.50
07/20/99
3.80
07/19/00
13.00
07/20/01
4.10
07/21 /97
5.50
07/21 /98
6.60
07/21 /99
3.80
07/20/00
13.00
07/21 /01
4.00
07/22/97
6.50
07/22/98
6.70
07/22/99
3.90
07/21 /00
13.00
07/22/01
4.00
07/23/97
37.00
07/23/98
7.10
07/23/99
3.70
07/22/00
13.00
07/23/01
4.00
07/24/97
290.00
07/24/98
6.90
07/24/99
3.20
07/23/00
12.00
07/24/01
8.00
07/25/97
261.00
07/25/98
25.00
07/25/99
3.20
07/24/00
80.00
07/25/01
16.00
07/26/97
19.00
07/26/98
15.00
07/26/99
3.30
07/25/00
36.00
07/26/01
18.00
07/27/97
9.00
07/27/98
8.20
07/27/99
3.40
07/26/00
18.00
07/27/01
90.00
07/28/97
9.50
07/28/98
12.00
07/28/99
3.50
07/27/00
12.00
07/28/01
18.00
07/29/97
8.50
07/29/98
7.70
07/29/99
3.60
07/28/00
12.00
07/29/01
4.00
07/30/97
8.30
07/30/98
9.90
07/30/99
3.60
07/29/00
11.00
07/30/01
5.00
07/31 /97
8.50
07/31 /98
12.00
07/31 /99
3.10
07/30/00
21.00
07/31 /01
3.80
08/01 /97
7.60
08/01 /98
7.90
08/01 /99
3.00
07/31 /00
14.00
08/01 /01
3.00
08/02/97
6.30
08/02/98
6.30
08/02/99
3.20
08/01 /00
21.00
08/02/01
2.60
08/03/97
5.80
08/03/98
6.30
08/03/99
3.40
08/02/00
107.00
08/03/01
3.10
08/04/97
6.70
08/04/98
6.10
08/04/99
3.40
08/03/00
28.00
08/04/01
3.60
08/05/97
8.10
08/05/98
5.90
08/05/99
3.90
08/04/00
20.00
08/05/01
3.80
08/06/97
8.80
08/06/98
5.90
08/06/99
3.20
08/05/00
198.00
08/06/01
4.20
08/07/97
6.80
08/07/98
6.00
08/07/99
2.60
08/06/00
71.00
08/07/01
4.20
08/08/97
6.50
08/08/98
6.00
08/08/99
3.10
08/07/00
13.00
08/08/01
4.20
08/09/97
5.60
08/09/98
6.10
08/09/99
3.60
08/08/00
10.00
08/09/01
3.80
08/10/97
5.50
08/10/98
14.00
08/10/99
3.50
08/09/00
9.50
08/10/01
3.80
08/11/97
6.40
08/11/98
16.00
08/11/99
3.60
08/10/00
14.00
08/11/01
7.70
08/12/97
6.50
08/12/98
8.30
08/12/99
3.40
08/11/00
11.00
08/12/01
87.00
08/13/97
6.50
08/13/98
7.20
08/13/99
3.60
08/12/00
8.80
08/13/01
34.00
08/14/97
6.60
08/14/98
6.50
08/14/99
8.50
08/13/00
7.70
08/14/01
32.00
08/15/97
6.60
08/15/98
5.50
08/15/99
15.00
08/14/00
8.10
08/15/01
18.00
08/16/97
5.70
08/16/98
5.80
08/16/99
5.00
08/15/00
9.30
08/16/01
11.00
08/17/97
5.60
08/17/98
32.00
08/17/99
4.00
08/16/00
11.00
08/17/01
11.00
08/18/97
6.20
08/18/98
9.50
08/18/99
4.00
08/17/00
9.70
08/18/01
11.00
08/19/97
6.10
08/19/98
7.40
08/19/99
3.40
08/18/00
9.60
08/19/01
12.00
08/20/97
6.30
08/20/98
6.40
08/20/99
3.20
08/19/00
8.70
08/20/01
13.00
08/21 /97
7.40
08/21 /98
6.10
08/21 /99
2.80
08/20/00
8.20
08/21 /01
14.00
08/22/97
6.60
08/22/98
5.50
08/22/99
2.40
08/21 /00
8.80
08/22/01
11.00
08/23/97
5.60
08/23/98
5.40
08/23/99
2.70
08/22/00
9.30
08/23/01
10.00
08/24/97
5.10
08/24/98
5.90
08/24/99
3.00
08/23/00
9.30
08/24/01
23.00
08/25/97
5.80
08/25/98
6.30
08/25/99
4.70
08/24/00
9.80
08/25/01
12.00
08/26/97
6.00
08/26/98
9.00
08/26/99
41.00
08/25/00
9.80
08/26/01
9.80
08/27/97
6.00
08/27/98
6.70
08/27/99
33.00
08/26/00
9.00
08/27/01
9.90
08/28/97
6.00
08/28/98
6.60
08/28/99
6.00
08/27/00
28.00
08/28/01
14.00
08/29/97
5.80
08/29/98
5.90
08/29/99
3.30
08/28/00
17.00
08/29/01
12.00
08/30/97
5.30
08/30/98
8.70
08/30/99
3.00
08/29/00
11.00
08/30/01
38.00
08/31 /97
5.10
08/31 /98
6.30
08/31 /99
3.00
08/30/00
29.00
08/31 /01
188.00
09/01 /97
6.10
09/01 /98
6.20
09/01 /99
2.80
08/31 /00
26.00
09/01 /01
18.00
09/02/97
7.70
09/02/98
6.00
09/02/99
2.70
09/01 /00
16.00
09/02/01
16.00
09/03/97
6.30
09/03/98
8.50
09/03/99
2.70
09/02/00
11.00
09/03/01
11.00
09/04/97
5.90
09/04/98
106.00
09/04/99
3.10
09/03/00
11.00
09/04/01
10.00
09/05/97
5.70
09/05/98
45.00
09/05/99
627.00
09/04/00
21.00
09/05/01
10.00
09/06/97
5.20
09/06/98
7.20
09/06/99
1270.00
09/05/00
26.00
09/06/01
9.10
09/07/97
5.00
09/07/98
5.10
09/07/99
685.00
09/06/00
12.00
09/07/01
8.50
09/08/97
5.80
09/08/98
10.00
09/08/99
147.00
09/07/00
9.20
09/08/01
8.20
43

Northeast Creek Fecal Coliform TMDL
Appendix 2 continued
09/09/97
7.40
09/09/98
12.00
09/09/99
19.00
09/08/00
8.50
09/09/01
9.40
09/10/97
14.00
09/10/98
6.20
09/10/99
77.00
09/09/00
8.00
09/10/01
11.00
09/11/97
45.00
09/11/98
5.00
09/11/99
18.00
09/10/00
8.00
09/11/01
11.00
09/12/97
12.00
09/12/98
3.80
09/12/99
8.80
09/11/00
8.00
09/12/01
9.30
09/13/97
5.10
09/13/98
3.90
09/13/99
7.30
09/12/00
7.50
09/13/01
9.30
09/14/97
4.20
09/14/98
4.20
09/14/99
7.00
09/13/00
8.00
09/14/01
9.10
09/15/97
4.70
09/15/98
4.40
09/15/99
45.00
09/14/00
9.30
09/15/01
9.40
09/16/97
4.60
09/16/98
4.20
09/16/99
1940.00
09/15/00
12.00
09/16/01
8.60
09/17/97
4.30
09/17/98
4.40
09/17/99
337.00
09/16/00
7.80
09/17/01
8.90
09/18/97
4.30
09/18/98
4.20
09/18/99
35.00
09/17/00
7.80
09/18/01
8.80
09/19/97
4.20
09/19/98
3.60
09/19/99
15.00
09/18/00
8.90
09/19/01
8.70
09/20/97
3.70
09/20/98
3.50
09/20/99
11.00
09/19/00
11.00
09/20/01
8.60
09/21 /97
3.30
09/21 /98
4.10
09/21 /99
10.00
09/20/00
10.00
09/21 /01
9.50
09/22/97
3.80
09/22/98
4.30
09/22/99
124.00
09/21 /00
9.60
09/22/01
8.50
09/23/97
3.90
09/23/98
4.10
09/23/99
37.00
09/22/00
9.40
09/23/01
8.30
09/24/97
10.00
09/24/98
4.00
09/24/99
12.00
09/23/00
17.00
09/24/01
19.00
09/25/97
20.00
09/25/98
4.00
09/25/99
8.60
09/24/00
17.00
09/25/01
34.00
09/26/97
7.60
09/26/98
3.60
09/26/99
7.30
09/25/00
14.00
09/26/01
8.20
09/27/97
4.70
09/27/98
3.40
09/27/99
83.00
09/26/00
74.00
09/27/01
6.20
09/28/97
4.10
09/28/98
4.00
09/28/99
528.00
09/27/00
11.00
09/28/01
5.50
09/29/97
4.90
09/29/98
4.20
09/29/99
734.00
09/28/00
6.90
09/29/01
5.20
09/30/97
4.50
09/30/98
6.60
09/30/99
619.00
09/29/00
6.10
09/30/01
5.40
10/01 /97
4.40
10/01 /98
5.00
10/01 /99
161.00
09/30/00
6.00
10/01 /01
5.90
10/02/97
4.10
10/02/98
4.40
10/02/99
21.00
10/01 /00
5.80
10/02/01
6.20
10/03/97
4.10
10/03/98
3.60
10/03/99
12.00
10/02/00
6.40
10/03/01
6.40
10/04/97
3.50
10/04/98
3.70
10/04/99
10.00
10/03/00
6.10
10/04/01
6.50
10/05/97
3.30
10/05/98
4.60
10/05/99
9.30
10/04/00
5.80
10/05/01
6.60
10/06/97
3.70
10/06/98
4.50
10/06/99
8.80
10/05/00
5.90
10/06/01
8.20
10/07/97
4.00
10/07/98
4.40
10/07/99
8.10
10/06/00
5.70
10/07/01
9.30
10/08/97
4.30
10/08/98
42.00
10/08/99
7.60
10/07/00
5.00
10/08/01
7.30
10/09/97
4.20
10/09/98
116.00
10/09/99
6.80
10/08/00
4.70
10/09/01
7.10
10/10/97
4.40
10/10/98
15.00
10/10/99
7.20
10/09/00
5.20
10/10/01
7.30
10/11/97
3.80
10/11/98
7.00
10/11/99
16.00
10/10/00
5.20
10/11/01
7.50
10/12/97
3.50
10/12/98
5.80
10/12/99
11.00
10/11/00
5.00
10/12/01
7.40
10/13/97
4.00
10/13/98
5.40
10/13/99
8.90
10/12/00
4.70
10/13/01
7.20
10/14/97
4.50
10/14/98
5.20
10/14/99
9.20
10/13/00
4.40
10/14/01
10.00
10/15/97
6.10
10/15/98
5.10
10/15/99
8.90
10/14/00
4.10
10/15/01
63.00
10/16/97
5.10
10/16/98
5.00
10/16/99
7.50
10/15/00
3.90
10/16/01
11.00
10/17/97
4.80
10/17/98
4.30
10/17/99
25.00
10/16/00
4.70
10/17/01
8.10
10/18/97
4.00
10/18/98
4.30
10/18/99
204.00
10/17/00
4.80
10/18/01
7.20
10/19/97
40.00
10/19/98
5.30
10/19/99
47.00
10/18/00
4.90
10/19/01
6.80
10/20/97
35.00
10/20/98
6.10
10/20/99
19.00
10/19/00
4.80
10/20/01
6.50
10/21 /97
9.30
10/21 /98
5.80
10/21 /99
46.00
10/20/00
4.50
10/21 /01
6.30
10/22/97
7.40
10/22/98
6.00
10/22/99
23.00
10/21/00
4.50
10/22/01
7.20
10/23/97
6.80
10/23/98
6.40
10/23/99
14.00
10/22/00
4.50
10/23/01
7.60
10/24/97
6.30
10/24/98
6.10
10/24/99
11.00
10/23/00
5.00
10/24/01
7.70
10/25/97
5.50
10/25/98
6.00
10/25/99
10.00
10/24/00
4.80
10/25/01
8.00
10/26/97
6.20
10/26/98
6.60
10/26/99
10.00
10/25/00
4.70
10/26/01
7.90
10/27/97
12.00
10/27/98
6.80
10/27/99
10.00
10/26/00
4.40
10/27/01
7.20
10/28/97
8.10
10/28/98
6.80
10/28/99
10.00
10/27/00
4.10
10/28/01
7.10
10/29/97
6.60
10/29/98
7.00
10/29/99
10.00
10/28/00
3.60
10/29/01
7.50

Northeast Creek Fecal Coliform TMDL
Appendix 2 continued
10/30/97
6.20
10/30/98
7.00
10/30/99
9.30
10/29/00
3.30
10/30/01
7.80
10/31 /97
5.90
10/31 /98
6.20
10/31 /99
9.70
10/30/00
3.40
10/31 /01
7.70
11 /01 /97
11.00
11 /01 /98
6.10
11 /01 /99
11.00
10/31 /00
3.50
11 /01 /01
7.30
11 /02/97
12.00
11 /02/98
6.90
11 /02/99
15.00
11 /01 /00
3.50
11 /02/01
7.30
11 /03/97
9.80
11 /03/98
37.00
11 /03/99
18.00
11 /02/00
3.70
11 /03/01
6.50
11 /04/97
8.20
11 /04/98
22.00
11 /04/99
12.00
11 /03/00
3.90
11 /04/01
6.50
11 /05/97
7.20
11 /05/98
10.00
11 /05/99
11.00
11 /04/00
3.90
11 /05/01
7.20
11 /06/97
7.00
11 /06/98
7.30
11 /06/99
10.00
11 /05/00
4.50
11 /06/01
7.00
11 /07/97
7.00
11 /07/98
5.90
11 /07/99
10.00
11 /06/00
5.20
11 /07/01
7.10
11 /08/97
6.30
11 /08/98
5.70
11 /08/99
11.00
11 /07/00
5.50
11 /08/01
7.00
11 /09/97
5.90
11 /09/98
6.20
11 /09/99
11.00
11 /08/00
5.90
11 /09/01
6.80
11 /10/97
6.40
11 /10/98
6.50
11 /10/99
11.00
11 /09/00
6.20
11 /10/01
6.80
11/11/97
6.60
11/11/98
6.80
11/11/99
10.00
11/10/00
6.50
11/11/01
5.90
11 /12/97
6.90
11 /12/98
7.30
11 /12/99
10.00
11 /11 /00
6.50
11 /12/01
6.70
11/13/97
25.00
11/13/98
7.00
11/13/99
8.90
11/12/00
6.90
11/13/01
7.10
11/14/97
108.00
11/14/98
6.70
11/14/99
8.50
11/13/00
7.70
11/14/01
7.20
11/15/97
43.00
11/15/98
12.00
11/15/99
8.70
11/14/00
9.90
11/15/01
7.50
11/16/97
13.00
11/16/98
9.90
11/16/99
8.80
11/15/00
7.50
11/16/01
7.40
11/17/97
10.00
11/17/98
19.00
11/17/99
9.50
11/16/00
7.30
11/17/01
6.70
11/18/97
9.10
11/18/98
12.00
11/18/99
10.00
11/17/00
7.30
11/18/01
5.60
11/19/97
8.30
11/19/98
6.70
11/19/99
10.00
11/18/00
7.10
11/19/01
6.10
11 /20/97
7.50
11 /20/98
5.60
11 /20/99
10.00
11 /19/00
7.60
11 /20/01
6.30
11 /21 /97
8.20
11 /21 /98
4.80
11 /21 /99
10.00
11 /20/00
9.80
11 /21 /01
6.10
11 /22/97
259.00
11 /22/98
4.30
11 /22/99
10.00
11 /21 /00
8.70
11 /22/01
5.30
11 /23/97
155.00
11 /23/98
4.70
11 /23/99
10.00
11 /22/00
8.20
11 /23/01
4.80
11 /24/97
18.00
11 /24/98
4.90
11 /24/99
10.00
11 /23/00
7.40
11 /24/01
4.90
11 /25/97
12.00
11 /25/98
4.70
11 /25/99
9.60
11 /24/00
7.20
11 /25/01
4.80
11 /26/97
10.00
11 /26/98
4.90
11 /26/99
37.00
11 /25/00
16.00
11 /26/01
4.60
11 /27/97
8.60
11 /27/98
4.50
11 /27/99
146.00
11 /26/00
42.00
11 /27/01
4.30
11 /28/97
7.20
11 /28/98
4.00
11 /28/99
13.00
11 /27/00
6.80
11 /28/01
4.20
11 /29/97
6.60
11 /29/98
4.30
11 /29/99
5.20
11 /28/00
5.70
11 /29/01
4.20
11 /30/97
11.00
11 /30/98
5.00
11 /30/99
4.10
11 /29/00
5.50
11 /30/01
4.20
12/01 /97
18.00
12/01 /98
5.10
12/01 /99
3.70
11 /30/00
5.20
12/01 /01
3.90
12/02/97
12.00
12/02/98
4.90
12/02/99
3.20
12/01 /00
5.10
12/02/01
3.70
12/03/97
9.50
12/03/98
5.00
12/03/99
3.10
12/02/00
5.10
12/03/01
4.00
12/04/97
8.90
12/04/98
4.60
12/04/99
3.20
12/03/00
5.10
12/04/01
4.00
12/05/97
8.00
12/05/98
4.20
12/05/99
4.10
12/04/00
5.10
12/05/01
4.00
12/06/97
6.80
12/06/98
4.00
12/06/99
6.10
12/05/00
5.20
12/06/01
4.00
12/07/97
5.90
12/07/98
4.50
12/07/99
6.90
12/06/00
5.20
12/07/01
3.90
12/08/97
6.20
12/08/98
5.00
12/08/99
6.40
12/07/00
5.20
12/08/01
3.60
12/09/97
6.80
12/09/98
5.10
12/09/99
6.10
12/08/00
5.40
12/09/01
3.50
12/10/97
21.00
12/10/98
4.90
12/10/99
6.30
12/09/00
5.40
12/10/01
3.90
12/11/97
28.00
12/11/98
4.70
12/11/99
7.30
12/10/00
5.40
12/11/01
17.00
12/12/97
13.00
12/12/98
4.10
12/12/99
5.70
12/11/00
5.60
12/12/01
4.90
12/13/97
9.50
12/13/98
41.00
12/13/99
5.90
12/12/00
5.60
12/13/01
3.10
12/14/97
7.60
12/14/98
62.00
12/14/99
146.00
12/13/00
5.40
12/14/01
2.80
12/15/97
7.40
12/15/98
9.50
12/15/99
183.00
12/14/00
5.70
12/15/01
2.80
12/16/97
7.20
12/16/98
65.00
12/16/99
41.00
12/15/00
5.60
12/16/01
2.80
12/17/97
7.00
12/17/98
25.00
12/17/99
33.00
12/16/00
6.70
12/17/01
3.10
12/18/97
6.80
12/18/98
7.50
12/18/99
29.00
12/17/00
153.00
12/18/01
6.90
12/19/97
6.60
12/19/98
5.00
12/19/99
29.00
12/18/00
170.00
12/19/01
4.60
45

Northeast Creek Fecal Coliform TMDL
Appendix 2 continued
12/20/97
5.60
12/20/98
3.90
12/20/99
31.00
12/21 /97
5.00
12/21 /98
3.70
12/21 /99
30.00
12/22/97
37.00
12/22/98
3.50
12/22/99
33.00
12/23/97
73.00
12/23/98
4.70
12/23/99
30.00
12/24/97
31.00
12/24/98
87.00
12/24/99
28.00
12/25/97
80.00
12/25/98
229.00
12/25/99
27.00
12/26/97
24.00
12/26/98
30.00
12/26/99
26.00
12/27/97
57.00
12/27/98
8.20
12/27/99
26.00
12/28/97
118.00
12/28/98
6.00
12/28/99
27.00
12/29/97
31.00
12/29/98
5.00
12/29/99
27.00
12/30/97
26.00
12/30/98
4.70
12/30/99
27.00
12/31 /97
16.00
12/31 /98
4.40
12/31 /99
28.00
12/19/00
29.00
12/20/01
3.80
12/20/00
29.00
12/21 /01
3.70
12/21 /00
25.00
12/22/01
3.60
12/22/00
23.00
12/23/01
3.50
12/23/00
21.00
12/24/01
3.80
12/24/00
20.00
12/25/01
3.90
12/25/00
19.00
12/26/01
3.90
12/26/00
19.00
12/27/01
4.10
12/27/00
19.00
12/28/01
4.10
12/28/00
19.00
12/29/01
4.10
12/29/00
18.00
12/30/01
4.10
12/30/00
19.00
12/31 /01
4.30
12/31 /00
18.00
m

Northeast Creek Fecal Coliform TMDL
Appendix 3. Relationship between Flow and Velocity at the Ambient Station (3660000)
1.5
1
0.5
Y_
0
0
m
-0.5
0
J
-1
-1.5
.2
0 1 2 3 4 5 6 7 8 9
Log (Discharge)
The relationship is expressed by V = 0.325 Q 0.24 where V is velocity in ft and Q is
discharge rate in cfs. The coefficient of determination (R- Square) is 0.62. (Data Source:
USGS).
47

Northeast Creek Fecal Coliform TMDL
Appendix 4. Fecal coliform at Durham West Water Treatment Plant (WWTP).
Daily Fecal Coliform concentration and Flow data measured for the year 1997 through
2001.
Date
fecal Flow
Date
fecal Flow
Date
fecal Flow
#/100MI cfs
#/100MI cfs
#/100MI cfs
01_01_1997
17.00
4.48
01_01_1999
30.00
3.57
01_01_2001
124.00
3.91
01_02_1997
7.00
5.46
01_02_1999
6.00
12.15
01_02_2001
22.00
4.02
01_03_1997
2.00
5.53
01_03_1999
30.00
26.84
01_03_2001
11.00
4.86
01_04_1997
17.00
4.70
01_04_1999
30.00
7.33
01_04_2001
2.00
4.90
01_05_1997
17.00
5.01
01_05_1999
4.00
5.82
01_05_2001
1.00
4.78
01_06_1997
2.00
5.72
01_06_1999
6.00
5.82
01_06_2001
181.00
4.12
01_07_1997
9.00
5.39
01_07_1999
13.00
5.52
01_07_2001
181.00
4.33
01_08_1997
21.00
5.87
01_08_1999
9.00
5.00
01_08_2001
18.00
5.07
01_09_1997
54.00
21.27
01_09_1999
11.00
4.43
01_09_2001
7.00
5.45
01_10_1997
78.00
7.24
01_10_1999
30.00
4.12
01_10_2001
410.00
5.15
01_11_1997
17.00
5.36
01_11_1999
30.00
5.04
01_11_2001
2600.00
5.15
01_12_1997
17.00
5.03
01_12_1999
30.00
5.07
01_12_2001
145.00
5.46
01_13_1997
15.00
6.25
01_13_1999
15.00
5.20
01_13_2001
181.00
5.04
01_14_1997
12.00
5.89
01_14_1999
8.00
5.40
01_14_2001
181.00
4.69
01_15_1997
27.00
7.12
01_15_1999
6.00
6.05
01_15_2001
181.00
3.71
01_16_1997
42.00
9.14
01_16_1999
22.00
3.50
01_16_2001
45.00
5.04
01_17_1997
29.00
6.59
01_17_1999
10.00
8.22
01_17_2001
38.00
5.01
01_18_1997
17.00
4.94
01_18_1999
30.00
24.23
01_18_2001
43.00
5.07
01_19_1997
17.00
5.03
01_19_1999
30.00
6.87
01_19_2001
4.00
5.26
01_20_1997
17.00
6.19
01_20_1999
26.00
6.56
01_20_2001
181.00
5.37
01_21_1997
6.00
5.82
01_21_1999
12.00
6.11
01_21_2001
181.00
6.50
01_22_1997
6.00
6.43
01_22_1999
190.00
5.69
01_22_2001
34.00
4.10
01_23_1997
6.00
5.98
01_23_1999
11.00
15.18
01_23_2001
11.00
5.45
01_24_1997
3.00
6.62
01_24_1999
30.00
28.67
01_24_2001
40.00
5.69
01_25_1997
17.00
8.18
01_25_1999
30.00
13.85
01_25_2001
9.00
6.03
01_26_1997
17.00
5.04
01_26_1999
4.00
6.51
01_26_2001
38.00
5.23
01_27_1997
8.00
6.34
01_27_1999
8.00
6.45
01_27_2001
181.00
5.77
01_28_1997
2.00
9.25
01_28_1999
29.00
5.77
01_28_2001
181.00
4.55
01_29_1997
17.00
6.78
01_29_1999
210.00
5.89
01_29_2001
27.00
4.66
01_30_1997
5.00
6.76
01_30_1999
2.00
4.70
01_30_2001
31.00
5.63
01_31_1997
6.00
6.42
01_31_1999
30.00
4.16
01_31_2001
278.00
6.11
02_01_1997
340.00
5.37
02_01_1999
4.00
8.34
02_01_2001
24.00
5.35
02_02_1997
340.00
5.38
02_02_1999
22.00
6.44
02_02_2001
23.00
5.45
02_03_1997
4.00
6.21
02_03_1999
8.00
6.13
02_03_2001
151.00
5.77
02_04_1997
3.00
5.87
02_04_1999
3.00
5.88
02_04_2001
151.00
4.61
02_05_1997
340.00
5.96
02_05_1999
62.00
4.95
02_05_2001
55.00
4.38
02_06_1997
8.00
6.02
02_06_1999
683.00
4.98
02_06_2001
31.00
5.76
02_07_1997
11.00
6.12
02_07_1999
683.00
5.57
02_07_2001
41.00
5.48
02_08_1997
340.00
6.41
02_08_1999
94.00
5.51
02_08_2001
60.00
5.40
02_09_1997
340.00
5.46
02_09_1999
6000.00
5.51
02_09_2001
300.00
5.35
02_10_1997
21.00
6.24
02_10_1999
1200.00
5.31
02_10_2001
151.00
5.34
02_11_1997
26.00
6.21
02_11_1999
1170.00
5.55
02_11_2001
151.00
4.35
02_12_1997
99.00
5.90
02_12_1999
305.00
5.55
02_12_2001
27.00
4.72
02_13_1997
37.00
9.66
02_13_1999
683.00
4.21
02_13_2001
37.00
6.03
02_14_1997
207.00
13.07
02_14_1999
683.00
3.88
02_14_2001
58.00
6.30
02_15_1997
340.00
9.93
02_15_1999
4.00
4.98
02_15_2001
41.00
6.64
02_16_1997
340.00
6.89
02_16_1999
1310.00
5.31
02_16_2001
24.00
6.39
M.

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
02_17_1997
340.00
6.60 02_17_1999
1900.00
5.68 02_17_2001
151.00
10.78
02_18_1997
3.00
6.68 02_18_1999
40.00
6.47 02_18_2001
151.00
23.50
02_19_1997
24.00
6.29 02_19_1999
1060.00
8.42 02_19_2001
47.00
5.37
02_20_1997
17.00
6.54 02_20_1999
683.00
6.53 02_20_2001
46.00
6.28
02_21_1997
2150.00
6.67 02_21_1999
683.00
4.84 02_21_2001
21.00
6.16
02_22_1997
340.00
5.00 02_22_1999
14.00
5.66 02_22_2001
1900.00
5.79
02_23_1997
340.00
4.50 02_23_1999
72.00
5.55 02_23_2001
29.00
7.91
02_24_1997
7.00
5.86 02_24_1999
27.00
5.54 02_24_2001
151.00
6.19
02_25_1997
2640.00
5.78 02_25_1999
42.00
5.49 02_25_2001
151.00
5.55
02_26_1997
780.00
6.14 02_26_1999
320.00
5.32 02_26_2001
36.00
5.77
02_27_1997
78.00
6.22 02_27_1999
683.00
4.69 02_27_2001
173.00
6.25
02_28_1997
17.00
6.75 02_28_1999
568.00
4.83 02_28_2001
48.00
6.00
03_01_1997
218.00
5.73 03_01_1999
15.00
5.88 03_01_2001
31.00
5.96
03_02_1997
218.00
5.33 03_02_1999
136.00
5.74 03_02_2001
40.00
5.89
03_03_1997
46.00
6.85 03_03_1999
1200.00
5.59 03_03_2001
367.00
5.80
03_04_1997
400.00
6.13 03_04_1999
2100.00
5.21 03_04_2001
367.00
9.50
03_05_1997
380.00
6.87 03_05_1999
29.00
5.03 03_05_2001
13.00
18.58
03_06_1997
1070.00
6.63 03_06_1999
568.00
4.12 03_06_2001
33.00
7.36
03_07_1997
190.00
6.14 03_07_1999
568.00
3.76 03_07_2001
14.00
6.47
03_08_1997
218.00
4.96 03_08_1999
3200.00
5.09 03_08_2001
54.00
5.89
03_09_1997
218.00
4.88 03_09_1999
3600.00
5.18 03_09_2001
33.00
6.02
03_10_1997
380.00
6.26 03_10_1999
27.00
5.23 03_10_2001
367.00
5.48
03_11_1997
270.00
5.96 03_11_1999
220.00
5.60 03_11_2001
367.00
4.81
03_12_1997
250.00
6.02 03_12_1999
46.00
4.44 03_12_2001
480.00
4.78
03_13_1997
222.00
6.26 03_13_1999
568.00
4.02 03_13_2001
41.00
6.19
03_14_1997
600.00
7.63 03_14_1999
568.00
16.74 03_14_2001
210.00
7.41
03_15_1997
218.00
5.21 03_15_1999
92.00
21.04 03_15_2001
29.00
3.62
03_16_1997
218.00
4.82 03_16_1999
86.00
6.65 03_16_2001
45.00
6.19
03_17_1997
48.00
5.97 03_17_1999
35.00
6.28 03_17_2001
367.00
5.52
03_18_1997
27.00
6.57 03_18_1999
420.00
5.97 03_18_2001
367.00
4.47
03_19_1997
110.00
11.15 03_19_1999
69.00
5.34 03_19_2001
58.00
4.29
03_20_1997
80.00
8.01 03_20_1999
568.00
4.33 03_20_2001
136.00
5.32
03_21_1997
118.00
6.79 03_21_1999
568.00
26.29 03_21_2001
367.00
18.12
03_22_1997
218.00
5.30 03_22_1999
1040.00
13.57 03_22_2001
6200.00
28.14
03_23_1997
218.00
4.92 03_23_1999
74.00
6.56 03_23_2001
39.00
11.43
03_24_1997
20.00
5.83 03_24_1999
16.00
6.30 03_24_2001
54.00
7.27
03_25_1997
85.00
6.06 03_25_1999
20.00
6.19 03_25_2001
42.00
5.91
03_26_1997
23.00
6.13 03_26_1999
13.00
5.97 03_26_2001
55.00
5.60
03_27_1997
9.00
5.66 03_27_1999
568.00
4.66 03_27_2001
58.00
5.77
03_28_1997
218.00
5.92 03_28_1999
568.00
4.33 03_28_2001
56.00
5.82
03_29_1997
218.00
4.48 03_29_1999
6.00
6.17 03_29_2001
210.00
6.22
03_30_1997
218.00
4.10 03_30_1999
607.00
5.31 03_30_2001
510.00
27.45
03_31_1997
28.00
5.33 03_31_1999
9.00
5.57 03_31_2001
367.00
20.59
04_01_1997
104.00
5.74 04_01_1999
136.00
19.84 04_01_2001
135.00
4.21
04_02_1997
232.00
5.59 04_02_1999
423.00
7.98 04_02_2001
135.00
4.21
04_03_1997
52.00
5.38 04_03_1999
423.00
5.11 04_03_2001
25.00
7.44
04_04_1997
108.00
5.69 04_04_1999
423.00
4.81 04_04_2001
91.00
6.42
04_05_1997
43.00
4.64 04_05_1999
56.00
5.37 04_05_2001
600.00
5.72
04_06_1997
43.00
4.84 04_06_1999
36.00
5.42 04_06_2001
100.00
6.92
04_07_1997
4.00
5.46 04_07_1999
60.00
5.42 04_07_2001
54.00
6.11
04_08_1997
43.00
5.44 04_08_1999
230.00
5.26 04_08_2001
135.00
5.89

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
04_09_1997
7.00
5.30 04_09_1999
44.00
5.49 04_09_2001
91.00
6.68
04_10_1997
25.00
5.34 04_10_1999
423.00
4.21 04_10_2001
360.00
5.96
04_11_1997
20.00
5.24 04_11_1999
423.00
9.04 04_11_2001
40.00
5.68
04_12_1997
43.00
5.41 04_12_1999
38.00
5.68 04_12_2001
40.00
5.37
04_13_1997
43.00
4.59 04_13_1999
205.00
5.29 04_13_2001
57.00
4.60
04_14_1997
13.00
5.77 04_14_1999
29.00
5.21 04_14_2001
135.00
3.93
04_15_1997
4.00
5.48 04_15_1999
10.00
5.46 04_15_2001
135.00
4.02
04_16_1997
12.00
5.63 04_16_1999
8.00
5.18 04_16_2001
19.00
5.11
04_17_1997
12.00
5.65 04_17_1999
423.00
4.25 04_17_2001
84.00
5.43
04_18_1997
5.00
5.47 04_18_1999
423.00
4.19 04_18_2001
42.00
7.01
04_19_1997
43.00
4.17 04_19_1999
69.00
5.04 04_19_2001
21.00
5.94
04_20_1997
43.00
4.11 04_20_1999
380.00
4.92 04_20_2001
9.00
5.04
04_21_1997
7.00
6.00 04_21_1999
280.00
5.09 04_21_2001
135.00
4.60
04_22_1997
9.00
7.58 04_22_1999
2400.00
5.11 04_22_2001
135.00
4.50
04_23_1997
5.00
8.17 04_23_1999
1740.00
5.25 04_23_2001
91.00
5.37
04_24_1997
42.00
6.64 04_24_1999
423.00
3.84 04_24_2001
600.00
5.94
04_25_1997
22.00
6.08 04_25_1999
423.00
3.65 04_25_2001
73.00
5.86
04_26_1997
43.00
4.47 04_26_1999
160.00
5.42 04_26_2001
39.00
5.12
04_27_1997
43.00
7.32 04_27_1999
2600.00
5.18 04_27_2001
217.00
5.01
04_28_1997
165.00
12.93 04_28_1999
260.00
5.88 04_28_2001
135.00
4.33
04_29_1997
43.00
18.23 04_29_1999
120.00
14.71 04_29_2001
135.00
3.85
04_30_1997
9.00
6.97 04_30_1999
20.00
17.78 04_30_2001
185.00
5.26
05_01_1997
56.00
8.28 05_01_1999
129.00
4.90 05_01_2001
70.00
5.14
05_02_1997
5.00
6.70 05_02_1999
129.00
4.60 05_02_2001
220.00
5.14
05_03_1997
7.00
6.30 05_03_1999
7.00
5.43 05_03_2001
136.00
5.11
05_04_1997
39.00
5.25 05_04_1999
10.00
5.32 05_04_2001
110.00
5.09
05_05_1997
2.00
6.18 05_05_1999
20.00
5.46 05_05_2001
128.00
4.16
05_06_1997
8.00
6.22 05_06_1999
9.00
5.63 05_06_2001
128.00
3.98
05_07_1997
470.00
5.94 05_07_1999
20.00
5.72 05_07_2001
40.00
5.31
05_08_1997
6.00
5.83 05_08_1999
129.00
4.27 05_08_2001
9.00
4.77
05_09_1997
1.00
5.84 05_09_1999
129.00
4.08 05_09_2001
580.00
5.17
05_10_1997
39.00
4.37 05_10_1999
50.00
5.25 05_10_2001
118.00
6.25
05_11_1997
39.00
4.53 05_11_1999
23.00
5.06 05_11_2001
133.00
5.86
05_12_1997
6.00
5.64 05_12_1999
70.00
5.21 05_12_2001
128.00
5.42
05_13_1997
58.00
5.66 05_13_1999
53.00
5.28 05_13_2001
128.00
4.90
05_14_1997
17.00
6.04 05_14_1999
128.00
5.40 05_14_2001
44.00
5.38
05_15_1997
50.00
5.17 05_15_1999
129.00
3.70 05_15_2001
38.00
6.19
05_16_1997
13.00
5.08 05_16_1999
129.00
4.08 05_16_2001
410.00
6.70
05_17_1997
39.00
4.34 05_17_1999
64.00
5.09 05_17_2001
100.00
5.49
05_18_1997
39.00
4.09 05_18_1999
1200.00
5.34 05_18_2001
46.00
6.33
05_19_1997
9.00
5.66 05_19_1999
564.00
6.93 05_19_2001
128.00
5.18
05_20_1997
2.00
5.65 05_20_1999
5.00
5.48 05_20_2001
128.00
5.12
05_21_1997
9.00
5.18 05_21_1999
6.00
4.87 05_21_2001
33.00
6.24
05_22_1997
1.00
5.06 05_22_1999
129.00
4.56 05_22_2001
200.00
6.00
05_23_1997
3.00
4.86 05_23_1999
129.00
4.30 05_23_2001
72.00
5.32
05_24_1997
39.00
4.52 05_24_1999
72.00
5.09 05_24_2001
48.00
4.87
05_25_1997
39.00
4.91 05_25_1999
200.00
5.04 05_25_2001
220.00
5.34
05_26_1997
39.00
4.71 05_26_1999
11.00
5.14 05_26_2001
128.00
5.86
05_27_1997
110.00
5.48 05_27_1999
13.00
4.92 05_27_2001
128.00
4.39
05_28_1997
17.00
5.21 05_28_1999
52.00
4.36 05_28_2001
128.00
5.28
05_29_1997
4.00
5.34 05_29_1999
129.00
3.40 05_29_2001
80.00
5.79
50

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
05_30_1997
5.00
5.42 05_30_1999
129.00
3.30 05_30_2001
70.00
5.63
05_31_1997
39.00
4.51 05_31_1999
129.00
3.65 05_31_2001
34.00
5.43
06_01_1997
18.00
5.24 06_01_1999
36.00
4.83 06_01_2001
25.00
22.31
06_02_1997
3.00
6.71 06_02_1999
88.00
5.07 06_02_2001
102.00
11.56
06_03_1997
8.00
6.24 06_03_1999
4.00
5.12 06_03_2001
102.00
5.49
06_04_1997
18.00
6.00 06_04_1999
46.00
4.75 06_04_2001
28.00
6.10
06_05_1997
7.00
5.39 06_05_1999
113.00
4.47 06_05_2001
43.00
6.56
06_06_1997
23.00
5.82 06_06_1999
113.00
3.30 06_06_2001
136.00
6.45
06_07_1997
18.00
5.82 06_07_1999
4.00
5.18 06_07_2001
112.00
5.82
06_08_1997
18.00
4.34 06_08_1999
16.00
5.37 06_08_2001
500.00
6.30
06_09_1997
7.00
5.18 06_09_1999
23.00
6.07 06_09_2001
102.00
6.28
06_10_1997
71.00
5.46 06_10_1999
72.00
5.46 06_10_2001
102.00
3.93
06_11_1997
4.00
5.47 06_11_1999
5.00
5.26 06_11_2001
62.00
6.11
06_12_1997
9.00
6.12 06_12_1999
113.00
3.91 06_12_2001
8.00
5.96
06_13_1997
6.00
6.41 06_13_1999
113.00
3.98 06_13_2001
23.00
6.84
06_14_1997
18.00
4.32 06_14_1999
693.00
2.10 06_14_2001
23.00
19.77
06_15_1997
18.00
4.18 06_15_1999
19.00
4.69 06_15_2001
76.00
8.49
06_16_1997
1.00
4.18 06_16_1999
108.00
7.02 06_16_2001
102.00
6.10
06_17_1997
18.00
5.25 06_17_1999
81.00
5.35 06_17_2001
102.00
5.71
06_18_1997
4.00
5.82 06_18_1999
42.00
5.28 06_18_2001
25.00
6.08
06_19_1997
4.00
5.62 06_19_1999
113.00
4.50 06_19_2001
8.00
6.10
06_20_1997
13.00
5.62 06_20_1999
113.00
4.50 06_20_2001
23.00
5.77
06_21_1997
18.00
4.95 06_21_1999
13.00
5.37 06_21_2001
109.00
6.19
06_22_1997
18.00
4.67 06_22_1999
25.00
5.37 06_22_2001
31.00
6.67
06_23_1997
23.00
3.87 06_23_1999
111.00
5.23 06_23_2001
102.00
6.10
06_24_1997
4.00
5.80 06_24_1999
420.00
5.42 06_24_2001
102.00
6.10
06_25_1997
12.00
5.12 06_25_1999
98.00
5.62 06_25_2001
57.00
6.20
06_26_1997
56.00
6.00 06_26_1999
113.00
4.89 06_26_2001
210.00
6.03
06_27_1997
15.00
5.60 06_27_1999
113.00
9.73 06_27_2001
250.00
6.20
06_28_1997
18.00
4.17 06_28_1999
99.00
5.97 06_28_2001
220.00
6.03
06_29_1997
18.00
4.04 06_29_1999
174.00
5.97 06_29_2001
182.00
5.77
06_30_1997
64.00
5.50 06_30_1999
300.00
6.20 06_30_2001
102.00
5.77
07_01_1997
25.00
6.14 07_01_1999
213.00
6.36 07_01_2001
359.00
5.01
07_02_1997
7.00
5.90 07_02_1999
25.00
6.07 07_02_2001
360.00
5.38
07_03_1997
12.00
5.40 07_03_1999
113.00
4.29 07_03_2001
1700.00
5.52
07_04_1997
47.00
4.19 07_04_1999
113.00
4.36 07_04_2001
359.00
4.80
07_05_1997
47.00
4.02 07_05_1999
113.00
4.78 07_05_2001
530.00
6.03
07_06_1997
47.00
4.14 07_06_1999
18.00
5.82 07_06_2001
1000.00
4.83
07_07_1997
4.00
5.27 07_07_1999
6.00
5.69 07_07_2001
900.00
4.58
07_08_1997
3.00
5.27 07_08_1999
105.00
5.48 07_08_2001
359.00
5.32
07_09_1997
25.00
5.27 07_09_1999
56.00
5.93 07_09_2001
230.00
5.91
07_10_1997
45.00
5.54 07_10_1999
113.00
5.03 07_10_2001
280.00
5.62
07_11_1997
47.00
5.01 07_11_1999
113.00
4.94 07_11_2001
520.00
5.45
07_12_1997
47.00
3.74 07_12_1999
54.00
6.11 07_12_2001
249.00
4.90
07_13_1997
47.00
4.06 07_13_1999
83.00
6.78 07_13_2001
211.00
5.12
07_14_1997
134.00
5.38 07_14_1999
217.00
7.06 07_14_2001
263.00
4.08
07_15_1997
66.00
5.66 07_15_1999
105.00
6.33 07_15_2001
359.00
3.93
07_16_1997
14.00
6.51 07_16_1999
109.00
5.88 07_16_2001
176.00
5.34
07_17_1997
24.00
5.99 07_17_1999
113.00
4.70 07_17_2001
88.00
4.84
07_18_1997
9.00
5.99 07_18_1999
113.00
4.69 07_18_2001
97.00
5.99
07_19_1997
47.00
4.59 07_19_1999
266.00
5.99 07_19_2001
282.00
5.74
51

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
07_20_1997
47.00
4.48 07_20_1999
210.00
6.13 07_20_2001
4.00
5.01
07_21_1997
4.00
5.92 07_21_1999
195.00
6.07 07_21_2001
359.00
4.95
07_22_1997
27.00
7.09 07_22_1999
15.00
6.08 07_22_2001
359.00
4.12
07_23_1997
96.00
7.29 07_23_1999
292.00
5.57 07_23_2001
230.00
5.51
07_24_1997
47.00
14.25 07_24_1999
113.00
4.78 07_24_2001
95.00
5.79
07_25_1997
212.00
7.11 07_25_1999
113.00
4.53 07_25_2001
110.00
5.80
07_26_1997
84.00
5.49 07_26_1999
73.00
4.61 07_26_2001
200.00
7.61
07_27_1997
47.00
1.86 07_27_1999
204.00
5.48 07_27_2001
359.00
22.78
07_28_1997
47.00
7.34 07_28_1999
35.00
5.43 07_28_2001
359.00
4.47
07_29_1997
29.00
5.61 07_29_1999
40.00
5.71 07_29_2001
359.00
5.43
07_30_1997
115.00
5.98 07_30_1999
46.00
5.54 07_30_2001
359.00
5.89
07_31_1997
6.00
5.93 07_31_1999
113.00
4.60 07_31_2001
11.00
5.60
08_01_1997
28.00
5.53 08_01_1999
143.00
4.52 08_01_2001
151.00
5.94
08_02_1997
28.00
4.21 08_02_1999
73.00
5.03 08_02_2001
4.00
4.52
08_03_1997
28.00
4.25 08_03_1999
265.00
5.06 08_03_2001
73.00
5.20
08_04_1997
5.00
5.92 08_04_1999
1200.00
5.60 08_04_2001
151.00
4.94
08_05_1997
50.00
5.99 08_05_1999
73.00
5.32 08_05_2001
151.00
4.66
08_06_1997
28.00
5.26 08_06_1999
31.00
4.36 08_06_2001
11.00
5.80
08_07_1997
56.00
5.27 08_07_1999
143.00
4.19 08_07_2001
2.00
5.37
08_08_1997
2.00
5.19 08_08_1999
143.00
5.29 08_08_2001
320.00
5.72
08_09_1997
28.00
4.08 08_09_1999
40.00
5.29 08_09_2001
720.00
5.54
08_10_1997
28.00
4.13 08_10_1999
225.00
5.43 08_10_2001
28.00
5.37
08_11_1997
2.00
5.82 08_11_1999
80.00
5.32 08_11_2001
151.00
7.91
08_12_1997
21.00
5.89 08_12_1999
15.00
5.42 08_12_2001
151.00
6.70
08_13_1997
18.00
5.71 08_13_1999
14.00
5.49 08_13_2001
12.00
6.82
08_14_1997
25.00
5.95 08_14_1999
143.00
5.83 08_14_2001
28.00
6.00
08_15_1997
170.00
5.59 08_15_1999
143.00
4.69 08_15_2001
38.00
5.55
08_16_1997
28.00
4.95 08_16_1999
66.00
5.69 08_16_2001
43.00
5.85
08_17_1997
28.00
4.60 08_17_1999
29.00
6.03 08_17_2001
29.00
5.55
08_18_1997
9.00
5.73 08_18_1999
42.00
5.74 08_18_2001
151.00
5.32
08_19_1997
9.00
5.26 08_19_1999
23.00
5.69 08_19_2001
151.00
6.58
08_20_1997
23.00
5.85 08_20_1999
42.00
5.29 08_20_2001
100.00
3.78
08_21_1997
11.00
5.78 08_21_1999
143.00
4.44 08_21_2001
590.00
5.38
08_22_1997
4.00
5.27 08_22_1999
143.00
4.04 08_22_2001
510.00
5.42
08_23_1997
28.00
3.98 08_23_1999
45.00
5.59 08_23_2001
81.00
6.05
08_24_1997
28.00
3.93 08_24_1999
42.00
5.68 08_24_2001
151.00
4.97
08_25_1997
6.00
5.35 08_25_1999
91.00
6.93 08_25_2001
151.00
4.38
08_26_1997
30.00
5.25 08_26_1999
210.00
9.13 08_26_2001
151.00
4.97
08_27_1997
64.00
5.25 08_27_1999
310.00
6.16 08_27_2001
60.00
5.31
08_28_1997
14.00
5.61 08_28_1999
143.00
4.60 08_28_2001
140.00
6.08
08_29_1997
12.00
4.67 08_29_1999
143.00
4.60 08_29_2001
36.00
6.02
08_30_1997
28.00
3.91 08_30_1999
125.00
4.98 08_30_2001
43.00
19.74
08_31_1997
28.00
4.20 08_31_1999
106.00
4.98 08_31_2001
310.00
6.44
09_01_1997
69.00
4.31 09_01_1999
216.00
4.83 09_01_2001
181.00
5.57
09_02_1997
1.00
5.58 09_02_1999
142.00
5.01 09_02_2001
181.00
4.84
09_03_1997
4.00
5.47 09_03_1999
44.00
4.60 09_03_2001
181.00
4.87
09_04_1997
5.00
4.40 09_04_1999
423.00
12.55 09_04_2001
170.00
5.82
09_05_1997
5.00
4.73 09_05_1999
423.00
25.27 09_05_2001
385.00
5.93
09_06_1997
69.00
3.91 09_06_1999
423.00
29.23 09_06_2001
200.00
5.00
09_07_1997
69.00
3.87 09_07_1999
1200.00
21.74 09_07_2001
520.00
4.84
09_08_1997
8.00
5.23 09_08_1999
1200.00
8.97 09_08_2001
181.00
4.39
52

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
09_09_1997
42.00
6.14 09_09_1999
60.00
10.82 09_09_2001
181.00
4.83
09_10_1997
116.00
7.72 09_10_1999
78.00
6.62 09_10_2001
110.00
5.74
09_11_1997
112.00
6.25 09_11_1999
423.00
5.31 09_11_2001
340.00
4.69
09_12_1997
218.00
5.26 09_12_1999
423.00
4.87 09_12_2001
18.00
4.92
09_13_1997
69.00
3.99 09_13_1999
5.00
6.24 09_13_2001
49.00
4.66
09_14_1997
69.00
4.17 09_14_1999
102.00
7.23 09_14_2001
94.00
4.15
09_15_1997
3.00
5.44 09_15_1999
600.00
21.23 09_15_2001
181.00
4.15
09_16_1997
3.00
5.26 09_16_1999
423.00
27.66 09_16_2001
181.00
4.15
09_17_1997
6.00
5.23 09_17_1999
740.00
10.66 09_17_2001
181.00
4.94
09_18_1997
69.00
5.52 09_18_1999
447.00
9.05 09_18_2001
70.00
4.84
09_19_1997
3.00
5.50 09_19_1999
423.00
9.21 09_19_2001
12.00
4.75
09_20_1997
69.00
4.41 09_20_1999
171.00
7.50 09_20_2001
120.00
5.12
09_21_1997
69.00
3.61 09_21_1999
1200.00
9.41 09_21_2001
240.00
4.87
09_22_1997
69.00
4.81 09_22_1999
384.00
10.38 09_22_2001
181.00
4.39
09_23_1997
69.00
5.20 09_23_1999
52.00
6.20 09_23_2001
181.00
4.44
09_24_1997
68.00
6.50 09_24_1999
41.00
5.57 09_24_2001
10.00
7.26
09_25_1997
3.00
5.76 09_25_1999
423.00
4.75 09_25_2001
86.00
4.94
09_26_1997
6.00
5.32 09_26_1999
423.00
4.86 09_26_2001
390.00
4.66
09_27_1997
69.00
4.52 09_27_1999
112.00
26.60 09_27_2001
295.00
5.15
09_28_1997
69.00
4.52 09_28_1999
520.00
27.70 09_28_2001
155.00
4.90
09_29_1997
19.00
5.35 09_29_1999
1200.00
28.08 09_29_2001
181.00
4.55
09_30_1997
1100.00
4.97 09_30_1999
380.00
22.67 09_30_2001
181.00
4.50
10_01_1997
575.00
4.6510_01_1999
188.00
7.71 10_01_2001
8.00
5.38
10_02_1997
870.00
5.11 10_02_1999
47.00
5.60 10_02_2001
42.00
5.38
10_03_1997
720.00
4.74 10_03_1999
47.00
5.21 10_03_2001
23.00
5.00
10_04_1997
211.00
3.7310_04_1999
50.00
6.1610_04_2001
17.00
5.00
10_05_1997
211.00
3.91 10_05_1999
42.00
5.63 10_05_2001
63.00
5.26
10_06_1997
4.00
4.8710_06_1999
48.00
5.4610_06_2001
30.00
4.43
10_07_1997
3.00
5.21 10_07_1999
86.00
5.46 10_07_2001
30.00
3.84
10_08_1997
10.00
5.29 10_08_1999
92.00
4.97 10_08_2001
3.00
4.47
10_09_1997
4.00
5.28 10_09_1999
47.00
5.29 10_09_2001
7.00
4.58
10_10_1997
211.00
5.34 10_10_1999
47.00
5.29 10_10_2001
64.00
4.89
10_11_1997
211.00
3.87 10_11_1999
36.00
6.33 10_11_2001
155.00
5.00
10_12_1997
211.00
3.98 10_12_1999
50.00
5.60 10_12_2001
2.00
4.32
10_13_1997
211.00
4.61 10_13_1999
84.00
5.54 10_13_2001
30.00
4.10
10_14_1997
22.00
5.6210_14_1999
16.00
5.4910_14_2001
30.00
6.75
10_15_1997
64.00
4.98 10_15_1999
46.00
5.20 10_15_2001
82.00
5.15
10_16_1997
102.00
5.04 10_16_1999
47.00
4.69 10_16_2001
12.00
4.92
10_17_1997
5.00
4.57 10_17_1999
47.00
16.69 10_17_2001
2.00
4.70
10_18_1997
211.00
3.80 10_18_1999
11.00
11.37 10_18_2001
15.00
4.50
10_19_1997
211.00
6.24 10_19_1999
6.00
7.04 10_19_2001
18.00
4.69
10_20_1997
5.00
5.1410_20_1999
60.00
7.7710_20_2001
30.00
4.15
10_21_1997
121.00
5.33 10_21_1999
33.00
7.41 10_21_2001
30.00
4.41
10_22_1997
126.00
5.0510_22_1999
9.00
6.1410_22_2001
15.00
4.92
10_23_1997
27.00
4.8310_23_1999
47.00
5.2310_23_2001
25.00
5.18
10_24_1997
100.00
5.0010_24_1999
47.00
4.6310_24_2001
64.00
5.18
10_25_1997
211.00
4.40 10_25_1999
27.00
5.68 10_25_2001
1.00
4.72
10_26_1997
211.00
4.88 10_26_1999
26.00
5.74 10_26_2001
5.00
4.38
10_27_1997
54.00
5.10 10_27_1999
34.00
5.79 10_27_2001
30.00
4.13
10_28_1997
5.00
4.78 10_28_1999
25.00
5.48 10_28_2001
30.00
4.32
10_29_1997
190.00
4.9210_29_1999
23.00
5.4010_29_2001
11.00
4.32
53

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
10_30_1997
820.00
5.01
10_30_1999
47.00
4.78
10_30_2001
40.00
5.06
10_31_1997
600.00
5.0510_31_1999
47.00
4.5610_31_2001
27.00
4.97
11_01_1997
94.00
4.63
11_01_1999
22.00
5.55
11_01_2001
29.00
5.57
11_02_1997
94.00
4.16
11_02_1999
600.00
5.97
11_02_2001
56.00
5.60
11_03_1997
170.00
4.9011_03_1999
35.00
5.1811_03_2001
1283.00
4.55
11_04_1997
7.00
4.6811_04_1999
42.00
5.1811_04_2001
1283.00
4.25
11_05_1997
8.00
4.99
11_05_1999
12.00
5.46
11_05_2001
2.00
4.81
11_06_1997
5.00
4.86
11_06_1999
47.00
4.25
11_06_2001
64.00
4.84
11_07_1997
15.00
4.92
11_07_1999
47.00
4.29
11_07_2001
1300.00
4.63
11_08_1997
94.00
3.81
11_08_1999
16.00
5.45
11_08_2001
6000.00
4.75
11_09_1997
94.00
3.78
11_09_1999
27.00
5.37
11_09_2001
600.00
5.09
11_10_1997
94.00
4.65
11_10_1999
83.00
4.67
11_10_2001
6000.00
4.92
11_11_1997
94.00
4.8711_11_1999
14.00
5.3411_11_2001
1283.00
3.87
11_12_1997
25.00
5.5311_12_1999
18.00
4.9511_12_2001
1283.00
5.23
11_13_1997
20.00
5.78
11_13_1999
4.00
4.29
11_13_2001
32.00
5.57
11_14_1997
109.00
4.3311_14_1999
47.00
4.3811_14_2001
42.00
5.45
11_15_1997
94.00
4.71
11_15_1999
31.00
5.25
11_15_2001
30.00
5.25
11_16_1997
94.00
3.83
11_16_1999
5.00
5.25
11_16_2001
40.00
4.90
11_17_1997
76.00
4.9711_17_1999
7.00
5.2311_17_2001
1283.00
4.18
11_18_1997
50.00
4.82
11_18_1999
3.00
5.28
11_18_2001
1283.00
4.33
11_19_1997
2.00
5.02
11_19_1999
15.00
5.45
11_19_2001
1.00
4.95
11_20_1997
156.00
5.02
11_20_1999
47.00
4.35
11_20_2001
3.00
5.18
11_21_1997
730.00
8.75
11_21_1999
47.00
4.38
11_21_2001
550.00
5.04
11_22_1997
94.00
6.85
11_22_1999
10.00
5.34
11_22_2001
1283.00
3.79
11_23_1997
94.00
5.0811_23_1999
1.00
5.3811_23_2001
1283.00
4.33
11_24_1997
70.00
5.54
11_24_1999
3.00
5.06
11_24_2001
1283.00
4.52
11_25_1997
52.00
5.50
11_25_1999
47.00
4.10
11_25_2001
1283.00
4.60
11_26_1997
13.00
5.59
11_26_1999
47.00
16.08
11_26_2001
41.00
6.24
11_27_1997
94.00
3.20
11_27_1999
47.00
6.30
11_27_2001
6000.00
5.09
11_28_1997
94.00
3.9011_28_1999
47.00
4.4711_28_2001
4700.00
5.40
11_29_1997
94.00
4.02
11_29_1999
1.00
5.60
11_29_2001
100.00
5.15
11_30_1997
54.00
4.94
11_30_1999
56.00
5.45
11_30_2001
72.00
4.92
12_01_1997
16.00
10.7412_01_1999
17.00
5.4612_01_2001
118.00
4.07
12_02_1997
16.00
5.2212_02_1999
52.00
5.2812_02_2001
118.00
4.04
12_03_1997
51.00
5.61
12_03_1999
580.00
5.11
12_03_2001
96.00
5.71
12_04_1997
92.00
5.2412_04_1999
182.00
4.1612_04_2001
300.00
5.38
12_05_1997
132.00
4.7012_05_1999
182.00
4.4712_05_2001
110.00
4.49
12_06_1997
54.00
3.9212_06_1999
1200.00
4.4712_06_2001
210.00
4.90
12_07_1997
54.00
3.77
12_07_1999
6.00
5.66
12_07_2001
94.00
4.50
12_08_1997
40.00
5.1712_08_1999
10.00
5.3512_08_2001
118.00
3.87
12_09_1997
88.00
5.3812_09_1999
10.00
5.5212_09_2001
118.00
3.95
12_10_1997
168.00
6.3712_10_1999
203.00
5.4912_10_2001
34.00
5.65
12_11_1997
54.00
5.4212_11_1999
182.00
4.3612_11_2001
76.00
5.26
12_12_1997
56.00
5.7712_12_1999
182.00
4.3312_12_2001
85.00
5.89
12_13_1997
54.00
4.3612_13_1999
14.00
7.7712_13_2001
580.00
4.56
12_14_1997
54.00
4.11
12_14_1999
300.00
24.8312_14_2001
47.00
4.84
12_15_1997
126.00
5.0212_15_1999
25.00
6.2012_15_2001
118.00
3.82
12_16_1997
54.00
5.3012_16_1999
20.00
5.7612_16_2001
118.00
3.76
12_17_1997
21.00
5.20
12_17_1999
24.00
5.62
12_17_2001
16.00
5.06
12_18_1997
39.00
5.3012_18_1999
182.00
4.9712_18_2001
62.00
4.90
12_19_1997
18.00
4.8012_19_1999
182.00
4.8312_19_2001
3.00
5.04
54

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
12_20_1997
10.00
3.7812_20_1999
7.00
5.4912_20_2001
12_21_1997
54.00
3.8812_21_1999
1.00
5.4312_21_2001
12_22_1997
18.00
8.5612_22_1999
1.00
5.0912_22_2001
12_23_1997
21.00
5.65
12_23_1999
2.00
4.35 12_23_2001
12_24_1997
54.00
6.29
12_24_1999
182.00
3.76 12_24_2001
12_25_1997
54.00
4.97
12_25_1999
182.00
3.76 12_25_2001
12_26_1997
54.00
4.49
12_26_1999
182.00
3.70 12_26_2001
12_27_1997
54.00
10.1912_27_1999
182.00
3.7012_27_2001
12_28_1997
54.00
5.22
12_28_1999
840.00
4.24 12_28_2001
12_29_1997
3.00
6.0212_29_1999
340.00
4.4312_29_2001
12_30_1997
16.00
5.5612_30_1999
1.00
4.1012_30_2001
12_31_1997
100.00
4.92
12_31_1999
182.00
4.02 12_31_2001
01_01_1998
30.00
4.04
01_01_2000
91.00
3.65
01_02_1998
6.00
4.62
01_02_2000
91.00
3.81
01_03_1998
30.00
4.36
01_03_2000
5.00
5.07
01_04_1998
30.00
4.08
01_04_2000
5.00
6.22
01_05_1998
4.00
5.50
01_05_2000
15.00
5.11
01_06_1998
6.00
5.89
01_06_2000
3.00
5.32
01_07_1998
13.00
6.52
01_07_2000
0.90
5.34
01_08_1998
9.00
20.37
01_08_2000
91.00
4.46
01_09_1998
11.00
9.14
01_09_2000
91.00
5.83
01_10_1998
30.00
5.08
01_10_2000
7.30
5.48
01_11_1998
30.00
4.99
01_11_2000
17.30
5.46
01_12_1998
30.00
5.66
01_12_2000
5.50
6.20
01_13_1998
15.00
5.75
01_13_2000
7.30
5.89
01_14_1998
8.00
5.62
01_14_2000
1200.00
5.21
01_15_1998
6.00
13.33
01_15_2000
91.00
4.46
01_16_1998
22.00
26.97
01_16_2000
91.00
4.36
01_17_1998
10.00
8.55
01_17_2000
2.70
5.01
01_18_1998
30.00
5.92
01_18_2000
0.90
4.64
01_19_1998
30.00
18.47
01_19_2000
2.70
5.35
01_20_1998
26.00
9.16
01_20_2000
0.90
6.47
01_21_1998
12.00
7.09
01_21_2000
2.50
6.10
01_22_1998
190.00
8.47
01_22_2000
91.00
4.98
01_23_1998
11.00
22.00
01_23_2000
91.00
6.08
01_24_1998
30.00
8.38
01_24_2000
6.20
7.07
01_25_1998
30.00
5.83
01_25_2000
9.00
6.08
01_26_1998
4.00
6.51
01_26_2000
11.00
5.35
01_27_1998
8.00
22.57
01_27_2000
7.30
4.95
01_28_1998
29.00
15.81
01_28_2000
9.00
3.61
01_29_1998
210.00
8.44
01_29_2000
91.00
4.78
01_30_1998
2.00
7.15
01_30_2000
91.00
17.64
01_31_1998
30.00
5.61
01_31_2000
600.00
12.81
02_01_1998
92.00
5.20
02_01_2000
8.00
7.58
02_02_1998
46.00
6.32
02_02_2000
2.00
6.13
02_03_1998
10.00
16.17
02_03_2000
19.10
6.22
02_04_1998
570.00
19.72
02_04_2000
17.30
6.39
02_05_1998
29.00
10.68
02_05_2000
139.00
4.84
02_06_1998
10.00
7.44
02_06_2000
139.00
4.63
02_07_1998
92.00
6.21
02_07_2000
6.40
4.73
02_08_1998
92.00
5.30
02_08_2000
14.50
4.44
14.00 5.14
380.00 4.92
118.00 4.36
118.00 4.36
118.00 5.15
118.00 3.71
118.00 4.43
8.00 4.55
3.00 4.63
118.00 4.36
118.00 4.08
1.00 4.77
55

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
02_09_1998
13.00
6.13 02_09_2000
16.40
4.61
02_10_1998
12.00
6.08 02_10_2000
7.80
4.39
02_11_1998
42.00
6.59 02_11_2000
7.30
4.30
02_12_1998
4.00
6.41 02_12_2000
139.00
5.59
02_13_1998
6.00
5.87 02_13_2000
139.00
3.67
02_14_1998
92.00
4.87 02_14_2000
23.60
5.20
02_15_1998
92.00
4.73 02_15_2000
26.00
4.95
02_16_1998
5.00
15.80 02_16_2000
41.00
5.40
02_17_1998
44.00
27.23 02_17_2000
221.00
6.47
02_18_1998
4.00
12.00 02_18_2000
136.00
10.13
02_19_1998
4.00
7.28 02_19_2000
139.00
6.14
02_20_1998
4.00
6.29 02_20_2000
139.00
5.93
02_21_1998
92.00
5.16 02_21_2000
33.90
6.37
02_22_1998
92.00
5.22 02_22_2000
1040.00
6.53
02_23_1998
15.00
12.31 02_23_2000
240.00
5.68
02_24_1998
8.00
6.75 02_24_2000
757.00
5.60
02_25_1998
650.00
6.06 02_25_2000
228.00
5.38
02_26_1998
320.00
5.99 02_26_2000
139.00
5.52
02_27_1998
46.00
6.19 02_27_2000
139.00
15.86
02_28_1998
92.00
5.15 02_28_2000
34.00
13.24
03_01_1998
1249.00
4.83 02_29_2000
40.00
5.91
03_02_1998
2550.00
5.94 03_01_2000
26.00
5.94
03_03_1998
6000.00
5.57 03_02_2000
59.00
5.65
03_04_1998
6000.00
5.60 03_03_2000
44.00
5.29
03_05_1998
59.00
5.63 03_04_2000
75.00
4.73
03_06_1998
6000.00
5.49 03_05_2000
75.00
4.52
03_07_1998
1249.00
4.81 03_06_2000
340.00
5.35
03_08_1998
1249.00
19.34 03_07_2000
230.00
5.55
03_09_1998
132.00
16.56 03_08_2000
64.00
5.59
03_10_1998
15.00
6.81 03_09_2000
168.00
5.65
03_11_1998
48.00
6.45 03_10_2000
217.00
5.14
03_12_1998
164.00
4.70 03_11_2000
75.00
4.47
03_13_1998
740.00
5.82 03_12_2000
75.00
4.22
03_14_1998
1249.00
4.50 03_13_2000
38.00
5.11
03_15_1998
1249.00
5.38 03_14_2000
17.60
5.28
03_16_1998
4.00
12.13 03_15_2000
14.80
5.38
03_17_1998
52.00
11.88 03_16_2000
75.00
6.19
03_18_1998
174.00
26.71 03_17_2000
38.50
4.63
03_19_1998
1249.00
27.93 03_18_2000
28.00
3.70
03_20_1998
2120.00
27.05 03_19_2000
75.00
4.02
03_21_1998
183.00
27.25 03_20_2000
235.00
6.79
03_22_1998
1249.00
15.49 03_21_2000
21.00
7.54
03_23_1998
86.00
7.02 03_22_2000
24.00
6.08
03_24_1998
550.00
6.68 03_23_2000
15.00
5.49
03_25_1998
70.00
6.28 03_24_2000
45.00
6.17
03_26_1998
28.00
6.19 03_25_2000
75.00
3.76
03_27_1998
1249.00
5.76 03_26_2000
75.00
4.94
03_28_1998
1249.00
6.36 03_27_2000
12.00
6.89
03_29_1998
1249.00
3.33 03_28_2000
60.00
6.07
03_30_1998
1249.00
5.93 03_29_2000
25.00
5.32
03_31_1998
14.00
5.99 03_30_2000
14.50
5.11
56

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
04_01_1998
12.00
8.66 03_31_2000
1.60
5.00
04_02_1998
26.00
6.03 04_01_2000
28.00
4.10
04_03_1998
26.00
6.19 04_02_2000
28.00
4.10
04_04_1998
26.00
5.11 04_03_2000
16.60
4.05
04_05_1998
26.00
6.19 04_04_2000
19.60
5.71
04_06_1998
5.00
5.57 04_05_2000
6.00
5.11
04_07_1998
8.00
5.72 04_06_2000
4.90
4.36
04_08_1998
2.00
7.12 04_07_2000
7.60
4.97
04_09_1998
9.00
10.68 04_08_2000
28.00
4.83
04_10_1998
26.00
5.72 04_09_2000
28.00
5.03
04_11_1998
26.00
4.64 04_10_2000
7.00
5.62
04_12_1998
26.00
4.33 04_11_2000
91.00
5.86
04_13_1998
26.00
5.57 04_12_2000
28.00
5.60
04_14_1998
48.00
5.72 04_13_2000
42.00
4.81
04_15_1998
5.00
5.57 04_14_2000
33.00
5.18
04_16_1998
2.00
11.29 04_15_2000
28.00
5.25
04_17_1998
17.00
5.88 04_16_2000
28.00
5.80
04_18_1998
26.00
6.34 04_17_2000
12.00
4.70
04_19_1998
1.00
6.03 04_18_2000
91.00
9.31
04_20_1998
5.00
9.13 04_19_2000
43.00
13.69
04_21_1998
10.00
7.89 04_20_2000
12.20
5.51
04_22_1998
5.00
7.58 04_21_2000
28.00
5.25
04_23_1998
26.00
8.82 04_22_2000
28.00
4.75
04_24_1998
124.00
5.11 04_23_2000
28.00
3.93
04_25_1998
26.00
4.18 04_24_2000
16.30
3.82
04_26_1998
26.00
8.51 04_25_2000
10.70
5.15
04_27_1998
26.00
5.42 04_26_2000
4.00
5.04
04_28_1998
26.00
5.42 04_27_2000
30.00
5.48
04_29_1998
130.00
5.42 04_28_2000
56.00
5.71
04_30_1998
26.00
5.57 04_29_2000
28.00
6.39
05_01_1998
2.00
5.57 04_30_2000
28.00
5.26
05_02_1998
123.00
4.18 05_01_2000
101.00
4.58
05_03_1998
123.00
4.18 05_02_2000
9.00
5.25
05_04_1998
123.00
5.72 05_03_2000
18.00
5.21
05_05_1998
6.00
5.42 05_04_2000
50.00
5.12
05_06_1998
4.00
5.42 05_05_2000
11.00
4.95
05_07_1998
123.00
7.58 05_06_2000
125.00
4.94
05_08_1998
26.00
5.88 05_07_2000
125.00
4.38
05_09_1998
123.00
4.64 05_08_2000
25.00
4.29
05_10_1998
123.00
10.06 05_09_2000
73.00
5.29
05_11_1998
8.00
9.59 05_10_2000
336.00
5.20
05_12_1998
116.00
6.19 05_11_2000
460.00
5.42
05_13_1998
112.00
5.88 05_12_2000
147.00
4.87
05_14_1998
58.00
3.56 05_13_2000
125.00
5.38
05_15_1998
128.00
5.42 05_14_2000
125.00
4.16
05_16_1998
123.00
4.95 05_15_2000
187.00
5.11
05_17_1998
123.00
4.64 05_16_2000
566.00
3.87
05_18_1998
470.00
5.72 05_17_2000
62.00
5.01
05_19_1998
48.00
5.72 05_18_2000
92.00
5.17
05_20_1998
61.00
5.72 05_19_2000
166.00
5.06
05_21_1998
25.00
5.57 05_20_2000
125.00
4.50
57

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
05_22_1998
188.00
5.26 05_21_2000
125.00
3.98
05_23_1998
123.00
5.57 05_22_2000
22.00
4.55
05_24_1998
123.00
4.95 05_23_2000
136.00
5.37
05_25_1998
123.00
5.11 05_24_2000
21.00
5.51
05_26_1998
78.00
6.03 05_25_2000
152.00
5.23
05_27_1998
310.00
6.03 05_26_2000
84.00
5.18
05_28_1998
560.00
5.72 05_27_2000
125.00
4.61
05_29_1998
15.00
5.88 05_28_2000
125.00
4.44
05_30_1998
123.00
4.64 05_29_2000
125.00
4.08
05_31_1998
123.00
4.64 05_30_2000
16.00
3.91
06_01_1998
105.00
6.30 05_31_2000
22.00
5.07
06_02_1998
85.00
5.80 06_01_2000
141.00
5.18
06_03_1998
84.00
6.95 06_02_2000
87.00
5.31
06_04_1998
26.00
6.48 06_03_2000
198.00
5.15
06_05_1998
4.00
6.56 06_04_2000
198.00
4.55
06_06_1998
460.00
4.83 06_05_2000
38.00
4.32
06_07_1998
460.00
4.27 06_06_2000
132.00
5.45
06_08_1998
410.00
5.62 06_07_2000
143.00
5.11
06_09_1998
84.00
5.68 06_08_2000
247.00
4.83
06_10_1998
52.00
5.99 06_09_2000
24.00
4.73
06_11_1998
232.00
6.03 06_10_2000
198.00
4.69
06_12_1998
26.00
5.88 06_11_2000
198.00
4.07
06_13_1998
460.00
4.56 06_12_2000
214.00
4.12
06_14_1998
460.00
4.46 06_13_2000
59.00
5.04
06_15_1998
3420.00
6.47 06_14_2000
168.00
5.07
06_16_1998
27.00
6.00 06_15_2000
200.00
5.29
06_17_1998
2360.00
5.82 06_16_2000
218.00
5.31
06_18_1998
1216.00
5.79 06_17_2000
198.00
5.25
06_19_1998
14.00
5.69 06_18_2000
198.00
4.19
06_20_1998
460.00
4.60 06_19_2000
550.00
4.18
06_21_1998
460.00
4.50 06_20_2000
340.00
5.51
06_22_1998
96.00
5.99 06_21_2000
187.00
5.54
06_23_1998
427.00
6.19 06_22_2000
269.00
5.65
06_24_1998
950.00
5.86 06_23_2000
184.00
5.49
06_25_1998
460.00
5.89 06_24_2000
198.00
5.54
06_26_1998
2.00
5.97 06_25_2000
198.00
4.13
06_27_1998
460.00
4.80 06_26_2000
223.00
4.15
06_28_1998
460.00
4.41 06_27_2000
41.00
5.29
06_29_1998
42.00
5.77 06_28_2000
420.00
5.63
06_30_1998
7.00
5.69 06_29_2000
243.00
6.10
07_01_1998
350.00
5.55 06_30_2000
237.00
6.10
07_02_1998
7.00
4.84 07_01_2000
427.00
5.72
07_03_1998
50.00
3.91 07_02_2000
427.00
3.73
07_04_1998
50.00
4.83 07_03_2000
88.00
3.54
07_05_1998
50.00
4.24 07_04_2000
427.00
4.13
07_06_1998
16.00
5.42 07_05_2000
68.00
3.79
07_07_1998
216.00
5.42 07_06_2000
70.00
5.18
07_08_1998
21.00
6.13 07_07_2000
224.00
5.14
07_09_1998
46.00
6.24 07_08_2000
427.00
5.04
07_10_1998
19.00
5.71 07_09_2000
427.00
4.15
07_11_1998
50.00
4.32 07_10_2000
97.00
4.66

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
07_12_1998
50.00
4.33 07_11_2000
251.00
5.52
07_13_1998
50.00
5.48 07_12_2000
122.00
5.49
07_14_1998
50.00
5.68 07_13_2000
101.00
5.52
07_15_1998
4.00
5.88 07_14_2000
71.00
5.31
07_16_1998
4.00
8.18 07_15_2000
427.00
5.86
07_17_1998
50.00
6.24 07_16_2000
427.00
4.56
07_18_1998
50.00
4.66 07_17_2000
1200.00
3.98
07_19_1998
50.00
4.87 07_18_2000
960.00
5.06
07_20_1998
4.00
5.79 07_19_2000
4800.00
5.51
07_21_1998
10.00
6.03 07_20_2000
281.00
5.45
07_22_1998
6.00
6.31 07_21_2000
5.00
5.04
07_23_1998
4.00
6.37 07_22_2000
45.00
5.31
07_24_1998
2.00
6.16 07_23_2000
427.00
4.04
07_25_1998
50.00
6.19 07_24_2000
158.00
7.54
07_26_1998
50.00
5.14 07_25_2000
8.00
10.01
07_27_1998
89.00
6.54 07_26_2000
6.00
6.31
07_28_1998
42.00
6.31 07_27_2000
155.00
5.69
07_29_1998
97.00
6.17 07_28_2000
44.00
5.54
07_30_1998
4.00
6.59 07_29_2000
427.00
5.31
07_31_1998
10.00
5.88 07_30_2000
427.00
6.20
08_01_1998
141.00
4.27 07_31_2000
220.00
5.85
08_02_1998
141.00
4.30 08_01_2000
480.00
6.36
08_03_1998
35.00
5.46 08_02_2000
530.00
10.77
08_04_1998
58.00
5.31 08_03_2000
81.00
11.74
08_05_1998
64.00
5.29 08_04_2000
132.00
7.29
08_06_1998
188.00
5.65 08_05_2000
267.00
11.79
08_07_1998
16.00
5.66 08_06_2000
267.00
16.28
08_08_1998
141.00
4.89 08_07_2000
133.00
5.01
08_09_1998
141.00
5.03 08_08_2000
22.00
6.02
08_10_1998
33.00
6.96 08_09_2000
91.00
5.86
08_11_1998
13.00
6.10 08_10_2000
225.00
6.07
08_12_1998
210.00
5.72 08_11_2000
760.00
6.16
08_13_1998
82.00
5.80 08_12_2000
267.00
5.45
08_14_1998
155.00
5.29 08_13_2000
267.00
4.21
08_15_1998
141.00
4.55 08_14_2000
86.00
3.84
08_16_1998
141.00
5.71 08_15_2000
50.00
5.46
08_17_1998
101.00
6.02 08_16_2000
165.00
7.64
08_18_1998
123.00
5.76 08_17_2000
360.00
6.81
08_19_1998
208.00
5.28 08_18_2000
174.00
5.55
08_20_1998
72.00
5.20 08_19_2000
267.00
5.68
08_21_1998
30.00
5.06 08_20_2000
267.00
4.53
08_22_1998
141.00
4.39 08_21_2000
535.00
4.04
08_23_1998
141.00
4.43 08_22_2000
530.00
5.37
08_24_1998
103.00
5.69 08_23_2000
410.00
5.09
08_25_1998
68.00
5.89 08_24_2000
455.00
5.17
08_26_1998
198.00
5.91 08_25_2000
595.00
5.63
08_27_1998
78.00
5.99 08_26_2000
9.00
5.49
08_28_1998
12.00
5.66 08_27_2000
267.00
4.53
08_29_1998
141.00
7.36 08_28_2000
85.00
6.36
08_30_1998
141.00
2.20 08_29_2000
305.00
6.08
08_31_1998
1120.00
5.62 08_30_2000
77.00
6.27
59

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
09_01_1998
72.00
5.35 08_31_2000
109.00
7.18
09_02_1998
600.00
5.86 09_01_2000
690.00
6.90
09_03_1998
1940.00
18.10 09_02_2000
178.00
6.41
09_04_1998
37.00
3.90 09_03_2000
178.00
5.60
09_05_1998
327.00
4.81 09_04_2000
178.00
5.23
09_06_1998
327.00
4.75 09_05_2000
218.00
6.16
09_07_1998
327.00
4.75 09_06_2000
163.00
6.08
09_08_1998
44.00
6.05 09_07_2000
167.00
5.29
09_09_1998
116.00
5.49 09_08_2000
90.00
5.28
09_10_1998
36.00
5.26 09_09_2000
178.00
5.23
09_11_1998
18.00
5.26 09_10_2000
178.00
4.55
09_12_1998
327.00
4.29 09_11_2000
199.00
4.36
09_13_1998
327.00
4.43 09_12_2000
295.00
6.07
09_14_1998
92.00
5.72 09_13_2000
420.00
4.77
09_15_1998
42.00
5.89 09_14_2000
231.00
5.85
09_16_1998
45.00
5.80 09_15_2000
244.00
6.10
09_17_1998
25.00
5.88 09_16_2000
178.00
5.17
09_18_1998
640.00
5.57 09_17_2000
178.00
4.15
09_19_1998
327.00
4.27 09_18_2000
94.00
3.99
09_20_1998
327.00
4.35 09_19_2000
212.00
5.62
09_21_1998
80.00
5.69 09_20_2000
120.00
5.65
09_22_1998
56.00
5.77 09_21_2000
26.00
5.66
09_23_1998
22.00
5.11 09_22_2000
69.00
5.99
09_24_1998
420.00
5.38 09_23_2000
178.00
6.54
09_25_1998
1660.00
5.34 09_24_2000
178.00
4.08
09_26_1998
327.00
4.56 09_25_2000
28.00
5.09
09_27_1998
327.00
4.49 09_26_2000
59.00
7.95
09_28_1998
720.00
5.59 09_27_2000
53.00
6.54
09_29_1998
16.00
5.79 09_28_2000
69.00
5.59
09_30_1998
188.00
6.00 09_29_2000
73.00
5.29
10_01_1998
92.00
5.65 09_30_2000
175.00
5.12
10_02_1998
46.00
4.9710_01_2000
158.00
4.27
10_03_1998
192.00
4.41 10_02_2000
230.00
4.29
10_04_1998
192.00
3.9910_03_2000
335.00
4.98
10_05_1998
136.00
5.21 10_04_2000
230.00
5.09
10_06_1998
107.00
5.5510_05_2000
960.00
5.48
10_07_1998
135.00
5.52 10_06_2000
270.00
5.35
10_08_1998
2700.00
15.8910_07_2000
158.00
5.28
10_09_1998
71.00
6.39 10_08_2000
158.00
3.62
10_10_1998
192.00
4.56 10_09_2000
248.00
4.70
10_11_1998
192.00
4.1210_10_2000
265.00
3.51
10_12_1998
48.00
4.94 10_11_2000
82.00
4.78
10_13_1998
56.00
5.1210_12_2000
73.00
4.61
10_14_1998
48.00
5.1410_13_2000
66.00
4.81
10_15_1998
170.00
4.8710_14_2000
158.00
4.80
10_16_1998
62.00
4.90 10_15_2000
158.00
3.95
10_17_1998
192.00
3.8810_16_2000
45.00
4.18
10_18_1998
192.00
3.93 10_17_2000
14.00
4.94
10_19_1998
75.00
5.48 10_18_2000
32.00
5.09
10_20_1998
132.00
5.09 10_19_2000
82.00
5.09
10_21_1998
89.00
4.78 10_20_2000
45.00
4.75

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
10_22_1998
113.00
4.7810_21_2000
158.00
4.55
10_23_1998
23.00
4.92
10_22_2000
158.00
3.99
10_24_1998
192.00
4.30
10_23_2000
44.00
3.96
10_25_1998
192.00
4.02
10_24_2000
42.00
4.64
10_26_1998
70.00
5.07
10_25_2000
57.00
4.94
10_27_1998
14.00
5.00
10_26_2000
303.00
4.95
10_28_1998
25.00
5.15
10_27_2000
25.00
4.92
10_29_1998
10.00
4.9510_28_2000
158.00
4.77
10_30_1998
11.00
5.07
10_29_2000
158.00
4.08
10_31_1998
192.00
3.95
10_30_2000
14.00
3.74
11_01_1998
212.00
4.02
10_31_2000
7.00
4.81
11_02_1998
40.00
5.71
11_01_2000
25.00
4.84
11_03_1998
66.00
6.36
11_02_2000
12.00
4.89
11_04_1998
171.00
5.40
11_03_2000
54.00
4.94
11_05_1998
790.00
5.20
11_04_2000
124.00
4.72
11_06_1998
144.00
4.8911_05_2000
124.00
4.13
11_07_1998
212.00
4.10
11_06_2000
32.00
3.87
11_08_1998
212.00
4.13
11_07_2000
23.00
4.80
11_09_1998
126.00
5.4211_08_2000
69.00
4.73
11_10_1998
260.00
5.2311_09_2000
48.00
5.31
11_11_1998
26.00
4.8911_10_2000
20.00
5.01
11_12_1998
1090.00
4.89
11_11_2000
124.00
4.75
11_13_1998
136.00
4.6711_12_2000
124.00
4.10
11_14_1998
212.00
4.5311_13_2000
39.00
3.98
11_15_1998
212.00
4.33
11_14_2000
52.00
4.98
11_16_1998
91.00
6.03
11_15_2000
63.00
5.06
11_17_1998
172.00
5.57
11_16_2000
550.00
4.94
11_18_1998
101.00
5.00
11_17_2000
236.00
4.89
11_19_1998
208.00
5.07
11_18_2000
124.00
4.89
11_20_1998
46.00
5.11
11_19_2000
124.00
4.12
11_21_1998
212.00
3.99
11_20_2000
128.00
4.35
11_22_1998
212.00
3.78
11_21_2000
600.00
4.92
11_23_1998
290.00
4.98
11_22_2000
94.00
4.84
11_24_1998
132.00
4.80
11_23_2000
124.00
4.46
11_25_1998
29.00
4.6611_24_2000
124.00
3.42
11_26_1998
212.00
3.45
11_25_2000
124.00
3.93
11_27_1998
212.00
3.53
11_26_2000
124.00
5.82
11_28_1998
212.00
3.54
11_27_2000
124.00
4.64
11_29_1998
212.00
3.7811_28_2000
97.00
5.43
11_30_1998
104.00
5.00
11_29_2000
99.00
4.80
12011998
10.10
10.51
11302000
111.00
4.94
12_02_1998
48.00
10.1012_01_2000
57.00
5.15
12_03_1998
66.00
10.01
12_02_2000
124.00
5.32
12_04_1998
590.00
10.0312_03_2000
124.00
4.39
12_05_1998
107.00
10.0312_04_2000
38.00
3.99
12_06_1998
107.00
10.0312_05_2000
45.00
5.37
12_07_1998
44.00
10.5712_06_2000
34.00
5.31
12_08_1998
41.00
10.2912_07_2000
53.00
5.28
12_09_1998
15.00
10.1212_08_2000
57.00
5.38
12_10_1998
11.00
10.03
12_09_2000
124.00
5.04
12_11_1998
134.00
9.9512_10_2000
124.00
4.29
61

Northeast Creek Fecal Coliform TMDL
Appendix 4 continued
12_12_1998
107.00
9.9512_11_2000
14.00
4.30
12_13_1998
107.00
9.9512_12_2000
21.00
5.17
12_14_1998
108.00
10.2312_13_2000
36.00
4.73
12_15_1998
5.00
10.1812_14_2000
21.00
5.15
12_16_1998
124.00
9.84 12_15_2000
21.00
5.42
12_17_1998
35.00
9.9512_16_2000
124.00
5.04
12_18_1998
29.00
10.01 12_17_2000
124.00
8.45
12_19_1998
107.00
10.01 12_18_2000
43.00
6.76
12_20_1998
107.00
10.01 12_19_2000
14.00
6.76
12_21_1998
28.00
9.9612_20_2000
43.00
6.11
12_22_1998
34.00
10.0312_21_2000
14.00
5.40
12_23_1998
600.00
10.0612_22_2000
20.00
5.32
12_24_1998
107.00
10.0612_23_2000
124.00
4.94
12_25_1998
107.00
10.0612_24_2000
124.00
4.13
12_26_1998
107.00
10.0612_25_2000
124.00
3.99
12_27_1998
107.00
10.0612_26_2000
124.00
3.42
12_28_1998
18.00
10.2912_27_2000
13.00
4.04
12_29_1998
18.00
10.32 12_28_2000
11.00
4.60
12_30_1998
34.00
10.20 12_29_2000
3.00
4.55
12_31_1998
260.00
9.8612_30_2000
124.00
4.55
12_31_2000
124.00
4.15
62

Northeast Creek Fecal Coliform TMDL
Appendix 5. Fecal Coliform Sampling in Durham County, NC.
Concentration in Septic and Sand Filter Effluent
Street
Permit No.
Sample Date
FC
(#/100ml)
Bartlett Dr
no permit
12/13/99
5,500
Barclay Rd
NCG550571
12/14/99
discarded, beyond holding time
Sandlewood Rd
NCG550951
12/14/99
discarded, beyond holding time
Sandlewood Road
Not a septic system
12/14/99I
discarded, beyond holding time
Michael
NCG550851 & NCG550852
12/15/99
490,000
Michael Dr
NCG550818
12/15/99
5,800
Mineral Springs Rd
NCG550771
12/15/99
1,622
Redwood Rd
NCG550800
12/15/99
<100
Barclay Rd
NCG550571
1/12/00
46
Bartlett Dr
no permit
1/12/00
27,000
Sandlewood Rd
NCG550951
1/12/00
56,000
Michael
NCG550851 & NCG550852
2/17/00
2,500
Michael Dr
NCG550818
2/17/00
44
Mineral Springs Rd
NCG550771
2/17/00
11
Redwood Rd
NCG550800
2/17/00
70
Barclay Rd
NCG550571
2/23/00
4,000
Bartlett Dr
no permit
2/23/00
5,800
Michael
NCG550851 & NCG550852
2/23/00
1,733
Michael Dr
NCG550818
2/23/00
4,900
Mineral Springs Rd
NCG550771
2/23/00
5,700
Redwood Rd
NCG550800
2/23/00
400
Sandlewood Rd
NCG550951
2/23/00
>6,000
Biscayne Road
no permit
6/1/00
200,000
Dresden Drive
no permit
6/1/00
2,800
Edenton Lane
NCG550609
6/1/00
270
Farrington
NCG550785
611100
100
Brecknock Street
NCG550920
6/6/00
1,200
(Welcome Circle
Ino permit
1 6/6/001
1411
Ed Cook Road
NCG550574
6/7/00
180
Glover Road
NCG551022
6/7/00
880
Statistics
FC
Average 32,668
median 1,733
min 11
max 490,000
63

Northeast Creek Fecal Coliform TMDL
Appendix 6. Partial List of General NPDES Permits in Northeast Creek Watershed.
PERMIT
FACILITY
COUNTY
STREET
NCG550813
CANUTO, JUAN & MARGARITO
DURHAM
3826 ANGIER AVENUE
NCG140090
CHANDLER CONCRETE CO-PLT #608
DURHAM
1014 ELLIS ROAD
NCG550574
DEAN, THOMAS - RESIDENCE
DURHAM
1711 ED COOK ROAD
NCG550665
DICK PATTON REALTY
DURHAM
2023 EASTWOOD DRIVE
NCG080595
FEDEX GROUND
DURHAM
2530 S. TRI-CENTER BLVD
NCG550148
FLETCHER, THOMAS A. - RESIDENCE
DURHAM
1336 LYNLEY DRIVE
NCG050116
FOAM DESIGN, INC.
DURHAM
2425 S. ALSTON AVE.
NCG551020
FOX, BILLY E. - RESIDENCE
DURHAM
2802 GLOVER ROAD
NCG080082
GIANT CEMENT COMPANY
DURHAM
824 ELLIS ROAD PO BOX 11097
NCG060107
GLAXO WELLCOME INC-DURHAM/CORN
DURHAM
FIVE MOORE DRIVE
NCG550905
HIGHT, ROBERT/928 JONES CIR
DURHAM
928 JONES CIRCLE
NCG550893
HOWARD, LUCY/916 JONES CIR
DURHAM
916 JONES CIRCLE
NCG551022
INSCOE, WALLACE R. - RESIDENCE
DURHAM
2810 GLOVER ROAD
NCG030279
INTERNATIONAL BUSINESS MACHINE
DURHAM
3039 CORNWALLIS ROAD
NCG550932
JONES, J.P./922 JONES CIR
DURHAM
922 JONES CIRCLE
NCG030311
MOTOROLA, INC-MOS 15/DURHAM SI
DURHAM
3026 CORNWALLIS ROAD
NCS000046
NATIONAL SPECIALTY GASES
DURHAM
63 UNITED DR.
NCG550739
OLD DOMINION FREIGHT LINE, INC
DURHAM
1810 NEW RALEIGH ROAD
NCG550601
PERDERGRASS, MARY - RESIDENCE
DURHAM
1617 ED COOK ROAD
NCG080580
ROADWAY EXPRESS, INC. (T672)
DURHAM
920 ELLIS ROAD
NCG550624
ROGERS, JIMMY L. & LISA - RESIDENCE
DURHAM
1901 LEONARD DRIVE
NCG130010
SONOCO PROD CO-DURHAM
DURHAM
4619 INDUSTRY LANE
NCG140129
SOUTHERN EQUIPMENT CO-DUR #17
DURHAM
3411 APEX HWY
NCGIO0024
SOUTHSIDE AUTO PARTS, INC.
DURHAM
1915 RIDDLE ROAD
NCG020283
TRIANGLE BRICK CO-DURHAM
DURHAM
6523 APEX RD
NCG060087
TRIANGLE SERVICES CORPORATION
DURHAM
P. O. BOX 13448
NCG050016
VALASSIS INSERTS INC
DURHAM
4918 PROSPECTUS DRIVE
NCGIO0026
WAGNER AUTO SALVAGE, INC.
DURHAM
1818 ISENHOUR STREET
ZIP
27703
27703
27703
27713
27713
27703
27713
27703
27703
27709
27705
27705
27703
27709
27703
27709
27713
27703
27703
27703
27703
27713
27713
27713
27713
27709
27713
27713
o

Northeast Creek Fecal Coliform TMDL
Appendix 7. Estimated high fecal coliform (>_ 400) occurrence.
Fecal coliform occurrence in the ambient station, B3660000, during the study period, 1997
through 2001.
Fecal
Fecal
Fecal
Flow
Coliform Weather
Flow
Coliform Weather
Flow
Coliform Weather
Date
at SR1100
(#/100 ml) Conditions Date
at SR1100
(#/100 ml) Conditions
Date
at SR1100
(#/100 ml) Conditions
(cfs)
Geo. mean
(cfs)
Geo. mean
(cfs)
Geo. mean
01_30_1997
35
425.75wet
01_26_2000
53
502.55wet
05_02_2000
15
417.94dry
01_31_1997
39
426.35wet
01_27_2000
39
502.67wet
05_03_2000
14
404.82dry
02011997
29
426.76 wet
01282000
33
485.29 dry
05_04_2000
14
405.25 wet
02_02_1997
22
427.08 wet
01292000
20
467.26 dry
05_05_2000
14
405.38 wet
02_03_1997
19
411.27 dry
01
_30_2000
108
467.16 wet
05_06_2000
14
406.50 wet
02_04_1997
18
410.95 dry
01
_31
_2000
579
467.94 wet
05_07_2000
15
407.74 wet
02_04_1998
623
409.49 wet
02012000
224
468.64 wet
05_08_2000
15
407.01 wet
02_05_1998
449
431.39 wet
02_02_2000
101
469.89 wet
05_09_2000
16
405.02 wet
02_06_1998
170
437.93 wet
02_03_2000
67
454.29 dry
05_10_2000
16
406.40 wet
02_07_1998
41
422.29 dry
02_04_2000
99
454.55 wet
05_11
_2000
16
408.29 wet
02_08_1998
26
406.15 dry
02_05_2000
101
455.74 wet
05_12_2000
16
425.05 wet
11_13_1999
8.9
401.27 wet
02_06_2000
57
456.77 wet
05_13_2000
16
427.39 wet
11_14_1999
8.5
402.11 wet
02_07_2000
44
474.07wet
05_14_2000
16
427.51 wet
11_25_1999
9.6
401.99 wet
02_08_2000
39
457.88 dry
05_15_2000
16
426.78 wet
11_26_1999
37
418.60 wet
02_09_2000
35
441.00 dry
05_16_2000
17
425.59 wet
11_27_1999
146
423.50wet
02_10_2000
32
424.61 dry
05_17_2000
17
430.08wet
11_28_1999
13
425.80wet
02_11_2000
31
409.40dry
05_18_2000
17
428.41 wet
11_29_1999
5.2
423.90 wet
02_12_2000
68
410.33 wet
05_19_2000
16
426.51 wet
11_30_1999
4.1
406.81 dry
02_13_2000
181
425.63wet
05_20_2000
16
426.42wet
01092000
32
418.08 wet
02_14_2000
110
442.51 wet
05_21
_2000
16
441.78 wet
01102000
207
438.68 wet
02_15_2000
100
460.08 wet
05_22_2000
30
458.75 wet
01_11_2000
278
460.34wet
02_16_2000
37
444.31 dry
05_23_2000
17
474.93wet
01_12_2000
48
485.23 wet
02_17_2000
31
428.54 dry
05_24_2000
12
491.23 wet
01_13_2000
32
484.87wet
02_18_2000
86
429.31wet
05_25_2000
10
471.47dry
01_14_2000
28
467.57dry
02_19_2000
79
430.01 wet
05_26_2000
9.6
469.17wet
01_15_2000
25
450.63 dry
02_20_2000
38
429.58 wet
05_27_2000
8.3
464.73 wet
01_16_2000
24
434.56dry
02_21_2000
30
413.82dry
05_28_2000
8
460.98wet
01_17_2000
25
450.12 wet
04_15_2000
36
412.76 wet
05_29_2000
11
458.20 wet
01182000
25
449.88 wet
04_16_2000
31
415.06 wet
05_30_2000
12
455.16 wet
01192000
28
449.73 wet
04_17_2000
14
411.95 wet
05_31
_2000
10
452.37 wet
01_20_2000
43
450.05wet
04_18_2000
154
415.75wet
06_01_2000
9.2
449.94dry
01_21_2000
57
450.53wet
04_19_2000
70
419.68wet
06_02_2000
9
447.59dry
01_22_2000
32
450.46wet
04_20_2000
22
418.65wet
06_03_2000
7.9
429.72dry
01232000
36
450.14 wet
04212000
19
405.08 dry
06_04_2000
9.4
428.65 wet
01_24_2000
53
466.72 wet
04_30_2000
31
414.92 wet
06_05_2000
9.6
425.61 wet
01252000
65
484.35 wet
05012000
18
432.30 wet
06_06_2000
9.6
422.90 wet
65

Northeast Creek Fecal Coliform TMDL
Appendix 7 continued
Fecal
Flow Coliform Weather
Date at SR1100 (#/100 ml) Conditions Date
(cfs)
06_07_2000
8.6
420.58 wet
06_08_2000
8.3
417.94 wet
06_09_2000
8
400.16dry
08012000
21
411.49 wet
08_02_2000
107
431.74 wet
08_03_2000
28
449.76 wet
08_04_2000
20
466.98 wet
08_05_2000
198
471.61 wet
08_06_2000
71
475.44 wet
08_07_2000
13
474.09 wet
08_08_2000
10
454.45dry
08_09_2000
9.5
435.43dry
08_10_2000
14
434.61 wet
08112000
11
433.85 wet
08_12_2000
8.8
432.40 wet
08_13_2000
7.7
416.51 dry
09_14_2000
9.3
404.84 wet
09_15_2000
12
407.11 wet
09_16_2000
7.8
407.32 wet
09_17_2000
7.8
408.27 wet
09_18_2000
8.9
406.61 wet
09_19_2000
11
406.32 wet
09_20_2000
10
406.53 wet
09212000
9.6
404.99 wet
01_14_2001
22
410.15wet
01_15_2001
23
431.40wet
01_16_2001
23
430.13wet
01_17_2001
22
428.70wet
01_18_2001
23
428.52wet
01_19_2001
23
428.05wet
01_20_2001
50
428.88wet
01_21_2001
34
429.81 wet
01_22_2001
23
445.13wet
01_23_2001
20
444.17dry
01_24_2001
19
442.73dry
01_25_2001
18
441.86dry
Fecal
Flow Coliform Weather
at SR1100 (#/100 ml) Conditions
(cfs)
01_26_2001
17
440.88dry
01_27_2001
16
440.52wet
01_28_2001
16
440.20wet
01_29_2001
18
439.21 wet
01 _30_2001
21
438.46 wet
01 _31 _2001
22
438.36 wet
02_01 _2001
20
454.49 wet
02_02_2001
19
470.89 wet
02_03_2001
17
454.20 dry
02_04_2001
17
453.85 wet
02_05_2001
21
453.47 wet
02_06_2001
21
453.49 wet
02_07_2001
19
453.23 wet
02_08_2001
18
452.58 wet
02_09_2001
17
435.99 dry
02_10_2001
16
419.63 dry
02_11_2001
16
404.22dry

Northeast Creek Fecal Colifonn TMDL
Appendix 8. Public notice of draft Northeast Creek Fecal Coliform TMDL
Appendix 8.1. The Herald -Sun
AFF AVU OP PL%L vrzA-rJON
-SIMeof *4&dfl Cumlinq
LAmmlw of Durh4im
Dm nd A MJhLl being dirty AYMrn. Saks 1[Lor she L, dhe PnUpPQI CLcak or
'111Cburham ElerOMCfe, hC.. pUbli8hersflf The J-Sun. h newfpgxr
auhlished Ln ar-d of g4n" eimvla!ion in mid Cawr}', ; rsd [hat u notice of
which the annmd IS A [rue tupy- was penlb del In 5mid nLwspmper
nne iine on She 61h day of Maw.
L,bw /& "- ,
Sw(rrn Ib and R hprrlb-td he g a 11'1d Ihi3 8' Limy of jUy, 3M.
My-"mi,sm rNiia-� December II%, 2fk*
Duftun CA3m w, Nonh C amura
r%M. PAd- -
u W = �E—OW.
Lrurwo�r�u•��
r� i�rta�PgFofqQ I.o m
CL-A4p�l.a~W�sFY
: r41 ii1
■ i � �, -Nr -
rr o.,t
y%, 4 b 114A fj,
'1A M 4 k Y
�rj11I I I%hL'4
67

Northeast Creek Fecal Colifonn TMDL
Appendix 8.2 The Chatham News.
NORTH CARDLlNAL
CH14T%A#d WL)NTY
The Chatham lPrwis
AFFIDAVIT OF pL113LICATLDN
$attirr tma undersigned. o HoWyr ¢db1i: OF laid CDMI:y n-1d Sta9r. duly
t-r+niitBiPW, gisal'ilK and authDHmd by MW to &*T&LW - -IPA Pn"ear
MY ODDWW—
R L gron-aA Tmziner
qIW gulyr dMig gym. oepcmi Rid IFrrrt rhel h■ I*Wi IL
VA,b b"
b=Lir ar, RA Dai.abla CIsni.
IL�.�rIM. �i{jArrt. Pr awrrtfll� arr�q� —
rhvrlad Ie■9b r is K*ff4*—rr
of T•hq C4Fh6m Hags Publishir'p CrL_ hx. bgwlW III IN "11-11tn'1 CH a
rgpfjp5pv knrmn z; Tho Methom New& puNill.Nd, Irrhlnd, a-d entered fs
!�coetd {Ig* r4ii In the T4Nn 4t 5ilor GITy In mid Caar4y and Slain I1-41
N 1"h a ouihtriAd 10 Rl" d7I1 alildWit rid snrvrn slhlerW1. rhal lhd
notira or IeWl rd,rtarreomaarli, a Irue cwy vI which Q dull -had harflba woo-
gpubIht** in i•Iw ChMEMM NUNN 01, Il* 1`011b,04 r!97m:
e-Id Tlmr 1t;& said remweptir r1 yOij:h W.h nnfflm, pear, domfft"l. or
I%el g4vgnIRwncmt vres puhlidwd NAA Ut ilv rime of nr_h rd arilrW EUO
r..hIlpAUr+-1 a zwmgr�e Irh+r ingi ra11 4f the reGuim—arl! and r; R'Iti�rlL s
ar SemIrn 1-69F ter lha G,a ml Moulds of N rch Carollry NO vs O gLOR
iiad raves yda,Ip lhIII moarlmp of Sxtior, I -mu or Th4 Gawe aI SIatum
of Nath QrrRia
Thu tides d$v 91' _La^�
4-L
dlgipr r■ of r:avnwmkr*aftEAO
$roan to mW Iutaa:rltled tr icm "in. 'till ? -e=o-
day al}J� Jc'i
fw.•Jltiazr.�• ����+7��.
N&MV r,b I.
My Irxrnh: nuupI-w if a 7 L,,tae�y.--
hwlb lam.
Slift rt XafkT.rrM= f7
'i.7�i 41 rM Tens; m UM*
Lft a*
I rrrl I .7 1a Fti I C7 Mm 9,v r-
iY iu F*WDNN r"-Rhk hrrh C-0
YL Tt79 iw %LJ"'; M
I�u 4iFr Yr.2�1 �'P Id �Ym IS
Pu .i nirhdm " rme.•rtid�
arid. ridnD EIMrIL 1 .7r
B1WL�.Irrr, 4C rM LLWmi u�
Lin IAKL irr a vMWwKill P311M
IJF flX- kpLrin r N1o1 F>-Od]
wta 5M W m ar rrYnr131 rrmlglt}
Y'Y .la W P4 J7 w1f• Wrdr ram. r"
i eeyy¢y w 1RDL na a 4aA Mi•]
rid is _Tm
F`ygiiis naa 3rr� Im PIG uM''31
fthIr �Fvd�. rl kt. Om Am- �.
.. 1 T u�! rrrm Cores. PM•
rph PK ST7 msL-lurr
nlya•Iti
WV