Document mpMLLkreQXyx5X9Da56kBbdBB
UNITED STATES
AGENCY
ONMENTALPROTECTION
REGION 1
NEW ENGLAND REGIONAL LABORATORY
NORTH CHELMSFORD, MA 01863
Date:9/20/2024
Subject:Reconnaissance and Sampling Inspection Report
Clean Water Act - National Pollutant Discharge Elimination System
Worcester, MA
ANNADigitally signed
From:Anna Hatke, Inspectorby ANNA HATKE
Date: 2024.09.23
Laboratory Services and Applied Science Division (LSASD) HATKE
09: 30: 34-04'00 '
Field Services Branch (FSB)
Reviewed
By:Jerome Keefe, Investigations Team Leader
LSASD - FSBDate: 2024.09J. ER2 OM3 E KE0 EF9 E : Di5 gi1 ta: ll0 y 1 sig ne-d 0by4 J'ER0OM0E KE'EF
E
To:Todd Borci, Manager
Enforcement and Compliance Assurance Division (ECAD)
Water Compliance Section 1
CC:Douglas Koopman, Inspector
ECAD
I. Facility Information
A. Facility Name: City of Worcester, MA
B. Facility Location: Worcester, MA
C. Facility Contact: Jay J. Fink, Commissioner, Dept. of Public Works and Parks,
dpw@worcesterma.gov, (508) 929-1300
D. NPDES Permit ID: MAS010002 (MS4)
II. Background Information
A. Date / Start time of Reconnaissance inspection: 07/23/2024 9:05
B. Weather conditions: Overcast, spotted showers approx. 74 F
C. USEPA Representatives: Anna Hatke, Michelle Coombs, Ryan Leo
D. State / Local Representatives: N / A
A. Date / Start time of sampling inspection: 07/24/2024 9:00
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B. Weather conditions: Overcast, spotted showers, approx. 73 F
C. USEPA Representatives: Anna Hatke, Ryan Leo, Nafisah Ali
D. State / Local Representatives: N / A
E. Federally Enforceable Requirements Investigated: Stormwater discharges and certain
non - stormwater discharges from the Worcester, MA Municipal Separate Storm Sewer
Systems (MS4) are authorized by the National Pollutant Discharge Elimination System
(NPDES) General Permit for the Discharge of Stormwater from Small MS4 (hereinafter,
the Permit), issued by the Environmental Protection Agency (EPA) Region 1. The City
obtained coverage under the Permit with NPDES Permit ID MAS010002.
F. Pollutants Sampled: Pharmaceuticals and Personal Care Products (PPCPs), E.
coli / Enterococcus, Ammonia (nitrogen), Total Chlorine, and Surfactants
III. Disclaimer:
Unless otherwise noted, this report describes conditions at the facility / property as observed by
EPA inspector(s), and / or through records provided to and / or information reported to EPA
inspector(s) by facility representatives and as understood by the inspector(s). This report may not
capture all operations or activities ongoing at the time of the inspection. This report does not make
final determinations on potential areas of concern. Nothing in this report affects EPA's authorities
under federal statutes and regulations to pursue further investigation or action.
IV. Type and Purpose of Inspection(s)
The purpose of the reconnaissance inspection was to locate stormwater outfalls which discharge
into Coal Mine Brook, O'Hara Brook, Fitzgerald Brook, and Lake Quinsigamond, while noting
appearance, presence of flow, and access requirements for one or more sampling inspections.
The purpose of the compliance sampling inspection was to identify potential illicit connections or
illegal discharges within the Worcester, MA MS4 that may adversely impact the water quality in
Coal Mine Brook, Fitzgerald Brook, Poor Farm Brook, and Lake Quinsigamond. Samples were
collected from 7 locations in accordance with the FSB Investigations Team Stormwater Program
Plan.
V. Permittee Details
The City of Worcester occupies approximately 38.5 square miles in Worcester County, MA
approximately 39 miles east of Boston, MA. The city shares borders with the municipalities of
Holden and West Boylston to the north, Shrewsbury and North Grafton to the east, Millbury and
Auburn to the south, Paxton, and Leicester to the west. According to the 2020 U.S. Census, the
population of Worcester, MA was 206,518.
VI. 07/23/2024 Reconnaissance Inspection Summary
On July 23, 2024, EPA Inspectors Anna Hatke, Michelle Coombs, and Ryan Leo conducted an
unannounced reconnaissance inspection of the Worcester, MA MS4 at the locations described in
Section VIII, including locations described under the map of the sample locations. They were not
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accompanied by any city or state representatives. The inspection started near Great Brook Valley
Park, Worcester, MA at approximately 9:05. At the time of the inspection, the weather was
overcast and approximately 74 F.
According to the National Weather Service (NWS) for the Worcester Regional Airport (KORH)
the last precipitation event prior to the inspection occurred on 7/18, 2024, with 0.02 inches
recorded. There was not precipitation recorded within the 72 hours before the inspection.
According to the NWS, in the month (to date) of July, the area observed 1.3 inches of rain, which
is approximately 52% of the 30-year normal value of 2.49 inches. According to the US Drought
Monitor, as of July 23, 2024, Worcester County is experiencing no drought conditions.
VII. 07/24/2024 Sampling Inspection Summary
On July 24, 2024, Anna Hatke, Nafisah Ali, and Ryan Leo, (" the EPA Inspection Team ")
conducted an unannounced compliance sampling inspection of the Worcester, MA MS4 at the
locations described in Section VIII. They were not accompanied by any city or state
representatives. The inspection started near 180 Constitution Avenue, Worcester, MA at
approximately 9:05. At the time of the inspection, the weather was overcast and approximately 73
F.
According to the National Weather Service (NWS) for the Worcester Regional Airport (KORH)
the last precipitation event prior to the inspection occurred on 7/23, 2024, with 0.12 inches
recorded. There was not precipitation recorded within the 72 hours before the inspection.
According to the NWS, in the month (to date) of July, the area observed 1.42 inches of rain, which
is approximately 54% of the 30-year normal value of 2.62 inches. According to the US Drought
Monitor, as of July 23, 2024, Worcester County is experiencing no drought conditions.
The sampling locations described in Section VIII were field screened using test kits for ammonia
(nitrogen), surfactants, and total chlorine. In - situ measurements for specific conductivity, salinity,
and temperature were also measured using a YSI water quality meter and recorded. Field data
were recorded on field data sheets. Samples were delivered to and analyzed for E. coli,
Enterococcus, and PPCPs at the EPA New England Regional Laboratory (NERL) in North
Chelmsford, MA. Table 1 below summarizes the sampling and analytical data.
VIII. Description of Sampling Locations (in order of collection time)
Photographs depicting each sample location are included in Appendix A of this report.
LQ-08: One circular concrete outfall approximately 3.5 feet in diameter, preceding a
roughly 20-foot concrete flume, located at 180 Constitution Avenue. Discharge flow was
approximately 10 gallons per minute (" gpm ") into Poor Farm Brook. Sample was collected
at the mouth of the outfall. No odor was detected. Color was clear and turbidity was low.
Some organic particulates were observed. Dark green algae growth was observed on the
concrete flume. Fish were observed in the stream directly downstream of the outfall.
LQ-09: One half - circle concrete outfall, approximately 2.5 feet in diameter, located at the
beginning of a wetland and at the base of a large shopping center, located at 541 Lincoln
Street. Discharge flow was approximately < 1 gpm into a wetland that channeled into an
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unnamed stream / brook. Sample was collected at the mouth of the outfall. A musty odor
was detected. Color was clear and some particulate matter was observed. Green algae were
observed growing on rocks directly downstream of the outfall. The outfall was roughly
halfway submerged.
* LQ-10: One circular corrugated metal outfall, approximately 4 feet in diameter, preceding
a roughly 10-foot concrete slanted pad, located at 481 Lincoln Street. Discharge flow was
approximately 5 gpm into an un - named stream, which combines into Coal Mine Brook,
which discharges into Lake Quinsigamond. Sample was collected at the mouth of the
outfall. A slight musty odor was detected, and a slight breeze was noted. Color was clear-
brown, and turbidity was low. Some organic particulates were observed. Trash was strewn
around the outfall and directly downstream. Froth was seen at the base of the concrete pad,
downstream of the outfall.
* LQ-11UP: One of two circular concrete outfalls on either side of a concrete wall,
approximately 1.5 feet in diameter, emptying onto a concrete conveyance, located at 25
Laselle Avenue. This confluence of discharge from both outfalls is joined downstream by
the discharge from LQ-10. Discharge flow was approximately 20 gpm. Discharge
contributes into Coal Mine Brook, which discharges into Lake Quinsigamond. Sample was
collected at the mouth of the left - side outfall, looking up - stream. A sewage odor was
detected. Color was clear- brownish - yellow, turbidity was low, and some suspended
organic particulates were observed. Light rainfall began during the sampling at this outfall.
Outfall sampled was chosen based on the Worcester, MA stormwater sewer system map.
LQ-12: In - stream sample from the inside of a concrete stormwater conveyance structure
on the East side of a stone wall culvert at 240 Coburn Avenue. The flow from the concrete
conveyance structure is joined immediately downstream by Fitzgerald brook, convening
into one stream, which discharges into Lak Quinsigamond. Sample was collected
approximately 3 feet prior to the confluence. An earthy sewage smell was detected. Color
was clear and turbidity was low. No floatables were observed. Dark brown algae growth
was observed on the bottom of the concrete conveyance structure. Trash and grass
clippings were observed upstream of the outfall. Fitzgerald Brook, prior to the confluence
was mostly non - flowing.
* LQ-13: One circular concrete outfall approximately 2.5 feet in diameter located at North
High School- 150 Harrington Way that empties out onto a concrete flume approximately 3
feet long. The outfall was located at the base of an elevated parking lot. Discharge flow
was approximately < 1 gpm into wetland that feeds into Fitzgerald Brook which discharges
into Lake Quinsigamond. Sample was collected at the mouth of the outfall. A notable sour
and musty odor was detected. Color was clear - but slightly brown. Turbidity was low and
no suspended particulates were observed. Sand was observed to be piled at the base of the
concrete flume.
LQ-14: One circular concrete outfall at the base of a stone wall, approximately 3.5 feet in
diameter located approximately.08 miles Southeast of 376 Coburn Avenue on an unpaved
road and parallel to the commuter rail. Discharge flow was approximately 2 gpm into an
unnamed stream that discharges into Lake Quinsigamond. Sample was collected at the
mouth of the outfall. No notable odor was detected. Color was clear- brown and some
suspended particulates were observed. Garbage was observed to be instream directly
downstream of the outfall.
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Map of Sample Locations
Note: the locations on the map were estimated using Google Earth and are used for display
purposes only.
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LQ-08
LO-07
LO-09
LQ-10 LO-09B
LO-11
LQ-13 LQ
- 12
LO-14
LQ-15
Note:
LQ-07: Outfall was inaccessible.
LQ-09A / LQ-09B: Only one outfall identified and labeled as " LQ-09 ".
LQ-11: No flow. " LQ-11UP " taken upstream of LQ-11.
LQ-15: Outfall was inaccessible.
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Table 1: Summary of Sampling and Analytical Data
Site IDLQ-8LQ-09LQ-10LQ-11UPLQ-12
Location Sample Date 07/24/2024 07/24/2024 07/24/2024 07/24/2024 07/24/2024
Sample Time 9:05 9:47 10:20 11:20 12:25
Coordinates North42.308207 42.292486 42.293418 42.290417 42.263929
(decimal
degrees) West-71.771581 -71.770181 -71.777243 -71.776333 -71.759341
Salinity, ppt. 0.6 1.8 0.5 0.1 0.1
YSI Meter Temperature, C 17.7 17.3 18.9 25.6 18.8
Conductivity, 1213 3374 1009 224.8 123.5
Ammonia 0.25 0.0 0.25 0.15 0.25
Field TestTotal Chlorine 0.03 0.03 0.07 0.020.03
Kits (mg / L)
Surfactants 0.25 0.5 0.5 0.15 0.5
Bacteria
E. coli 626 1302 3080 30 -9678
(MPN / 100mL) Enterococcus30510457204611
Cotinine 2.5 0.54 18 3.6 62
Acetaminophen 26 ND 220 ND 300
Paraxanthine 5.5 ND 120 ND 62
PPCPs (ng / L)Atenolol ND ND 21 ND 6.5
Caffeine 13 6.0 1600 5.3 680
Abbreviations and Notes:
Metoprolol ND ND 5.9 ND 4.6
Diphenhydramine 0.52 ND 17 ND 7.6
Carbamazepine 0.61 ND 0.44 ND 2.0
1. The coordinates listed in Table 1 were derived from the map created in Google Earth, therefore the coordinates are estimates of the actual
locations.
N / A: Not Analyzed
ND: Not Detected above Reporting Limit
E. Coli / Fecal Coliform: Red > 10,000 col / 100ml, Orange > 1,260 col / 100ml, Yellow > 235 col / 100ml, Black < 235 col / 100ml
Entero: Red 1,000 col 100ml, Orange > 350, Yellow > 61 col / 100ml, Black < 61 col / 100ml
NH3: Red 6 mg / L, Orange > 0.5 mg / L, Yellow > 0.25 mg / L, Black < 0.25 mg / L
Cl2: Red 1.0 mg / l, Orange > 0.3 mg / L, Yellow > 0.02 mg / L, Black < 0.02 mg / L
Surfactants: Red 21.0 mg / L, Orange > 0.5 mg / L, Yellow > 0.25 mg / L, Black < 0.25 mg / L (may give false positive at salinity greater than 1 ppt)
PPCPs: Red 100x the RI, Orange > 10x the RL, Yellow > 3x the RL; Black < 3x the RL *
* See Reporting Limit (RL) values for each compound in attached Laboratory Report for Source Tracking
EPA notes while there are currently no numerical standards to compare pharmaceutical results against, it is EPA's experience that acetaminophen is the
single best bacterial source tracking compound of those listed above, and any detection of this compound may indicate a source of sanitary sewage. With
respect to all of the above compounds, when a sanitary sewage source is present, depending on the type of source, distance from the sample location, and
the strength of the source, concentrations of these compounds may range from the low ng / l range up to thousands of ng / L.
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Table 1: Summary of Sampling and Analytical Data, cont.
Site IDLQ-13LQ-14
Location Sample Date 07/24/2024 07/24/2024
Sample Time 12:54 13:47
Coordinates North42.262834 42.257660
(decimal
degrees)West
-71.766319 -71.758855
Salinity, ppt.0.00.2
YSI Meter Temperature, C21.716.0
Conductivity, 77.8 507
Field Test
Kits (mg / L)
Ammonia 0.25 0.25
Total Chlorine 0.03 0.00
Surfactants 0.75 1.0
Bacteria E. coli 512 1302
(MPN / 100mL) Enterococcus 3448 1607
Cotinine 3.8 18
Acetaminophen 3.0 46
Paraxanthine 6.1 23
PPCPs (ng / L)
Atenolol ND 4.5
Caffeine 240 170
Metoprolol ND 2.6
Diphenhydramine ND 3.6
Abbreviations and Notes:
Carbamazepine ND ND
1. The coordinates listed in Table 1 were derived from the map created in Google Earth, therefore the coordinates are estimates of the actual
locations.
N / A: Not Analyzed
ND: Not Detected above Reporting Limit
E. Coli / Fecal Coliform: Red 10.000 col / 100ml, Orange > 1,260 col / 100ml, Yellow > 235 col / 100ml, Black < 235 col / 100ml
Entero: Red 1,000 col / 100ml, Orange > 350 col / 100ml, Yellow > 61 col / 100ml, Black < 61 col / 100ml
NH3: Red 6 mg / L. Orange 0.5 mg / L, Yellow > 0.25 mg / L, Black < 0.25 mg / L
Ch2: Red 1.0 mg / l, Orange > 0.5 mg / L, Yellow > 0.02 mg / L, Black < 0.02 mg / L
Surfactants: Red 1.0 mg / L, Orange > 0.5 mg / L, Yellow > 0.25 mg / L, Black < 0.25 mg / L (may give false positive at salinity greater than 1 ppt)
PPCPs: Red 100x the RL, Orange > 10x the RL, Yellow > 3x the RL; No Pink < 3x the RL *
* See Reporting Limit (RL) values for each compound in attached Laboratory Report for Source Tracking
EPA notes while there are currently no numerical standards to compare pharmaceutical results against, it is EPA's experience that acetaminophen is the
single best bacterial source tracking compound of those listed above, and any detection of this compound may indicate a source of sanitary sewage. With
respect to all of the above compounds, when a sanitary sewage source is present, depending on the type of source, distance from the sample location, and
the strength of the source, concentrations of these compounds may range from the low ng / l range up to thousands of ng / L.
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IX. Appendix
Appendix A: Photograph Log
X. Attachments
Attachment A: Laboratory Report for PPCPs (Source Tracking) Analysis
Attachment B: Laboratory Report for E. coli Analysis
Attachment C: Laboratory Report for Enterococcus Analysis
End of Report
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Appendix A
Photograph Log
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Photo 1: LQ-08 (photo taken 07/24/2024 at approx. 9:05) Stream located near 180 Constitution
Avenue, discharging into Poor Farm Brook, upstream of Lake Quinsigamond. Sample point is indicated
by a red X.
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Photo 2: LQ-09 (photo taken 07/24/2024 at approx. 9:47) Stream located near 541 Lincoln Street,
discharging into a wetland with contributes into Coal Mine Brook, upstream of Lake Quinsigamond.
Sample point is indicated by a red X.
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Photo 3: LQ-10 (photo taken 07/24/2024 at approx. 10:20) Stream located near 481 Lincoln Street.
discharge contributes into Coal Mine Brook, which discharges into Lake Quinsigamond. Sample point is
indicated by a red X.
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Photo 4: LQ-11UP (photo taken 07/24/2024 at approx. 11:20) Stream located near 25 Laselle Avenue
Combined discharge contributes into Coal Mine Brook, which discharges into Lake Quinsigamond.
Sample point is indicated by a red X.
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Photo 5: LQ-12 (photo taken 07/24/2024 at approx. 12:25) Stream located near 240 Coburn Avenue,
discharging into Fitzgerald Brook, upstream of Lake Quinsigamond. Sample point is indicated by a red
X. LQ-12 flow is indicated by blue arrow'A '. Flow from Fitzgerald Brook is indicated by blue arrow
' B '.
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op
Photo 6: LQ-13 (photo taken 07/24/2024 at approx. 12:54) Stream located near North High School- 150
Harrington Way, discharging into a wetland which contributes into Fitzgerald Brook. Fitzgerald Brook
discharges into Lake Quinsigamond. Sample point is indicated by a red X.
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Photo 7: LQ-14 (photo taken 07/24/2024 at approx. 13:47) Stream located near 376 Coburn Avenue,
discharging into an unidentified brook, upstream of Lake Quinsigamond. Sample point is indicated by a
red X.
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Attachment A
Laboratory Report for
Source Tracking Analysis
Author: LSASD Laboratory Services Branch
Pages: 16
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Attachment B
Laboratory Report for
E. coli Analysis
Author: LSASD Laboratory Services Branch
Pages: 4
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Attachment C
Laboratory Report for
Enterococcus Analysis
Author: LSASD Laboratory Services Branch
Pages: 4
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End of Report
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