HomeMy Public PortalAboutBOH Packet 01.03.24Brewster Pressure Dose Systems
12/28/2023
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A B C D E F G H I J K L M N O P Q
Street #Street Name Owner Name Mailing Address Town Map Parcel Zone II Watershed GPD Inspection #1 Inspection #2 Inspection #3 Inspection #4 Letter sent 7/14/23 Responses
1 4 Alden Drive Jamie & Jennifer Dicandia 19 Adam Taylor Road Sterling, MA 01564 56 89 No CCB 288.7 X
2 Bay Pines System 9 (Ocean Edge)Ocean Edge 1 Villages Drive Brewster, MA 02631 No CCB 13040 X
3 9 & 11 Breakwater Road The Todd & Jessica French Nominee Trust, Wendy French, Trustee 258 Sheep Pond Drive Brewster, MA 02631 57 10 No CCB 356.97 X
4 141 Brewster Road (Brewster Senior Housing)Frederick Court Development Corp. 460 Main Street Hyannis, MA 02601 56 75-16925 No CCB 3600 X
5 200 Brier Lane Jack & Nancy Drake, Trustees Briar Lane Nom. Trust PO Box 935 Brewster, MA 02631 48 45 No CCB 440 10/18/2023 9/1/2022 9/10/2021 12/10/2020 Perc-Rite System
6 34 Captain Connolly Road Peter & Ellen Marie Guidry 1907 Stirrup Lane Alexandria, VA 22308 19 29 Yes HR 330 Perc-Rite System - no O & M contract
7 19 Cedar Hill Road Virginia B. Neumann, Trustee Virginia B. Neumann 2017 Trust 19 Charles Street Lexington, MA 02421 38 20 No CCB 341.88 12/6/2022 11/24/2021 12/10/2020 11/26/2019 X Perc-Rite System
8 94 Cedar Hill Road William & Maria Gaine 58 Kings Row Ashland, MA 01721 38 30 No CCB 444 X
9 102 Cedar Hill Road Jonathan Rosenfeld & Arlene Feldman 10 Ben Arthurs Way Dover, MA 02030 38 29 No CCB 336.7 X
10 40 Cranview Road Sanford & Madeline Zevon 40 Cranview Road Brewster, MA 02631 10 66 Yes HR 364 X
11 46 Featherbed Lane Boys Camp Inc., Camp Mitton Attn: Simon Hess 119 Myrtle Street Duxbury, MA 02332 11 45 Yes CCB 1500 X
12 121 Fiddlers Lane John & Christine Martell 46 Harjean Road Billerica, MA 01821 48 33 No CCB 356.98 X
13 169 Fiddlers Lane Joshua & Sarah Brunelle 169 Fiddlers Lane Brewster, MA 02631 48 35 No CCB 462.5 X
14 Fletcher Village System 2-1 (Ocean Edge)Ocean Edge 1 Villages Drive Brewster, MA 02631 No CCB 10780 X
15 11 Frederick Court Brewster Housing Authority 11 Frederick Court Brewster, MA 02631 56 67 No CCB 3649 X
11/13/23Email from Chad, Coastal
Eng. requesting clarification on
frequency of mandatory inspections
16 1000 Freeman's Way Town of Brewster 1000 Freemans Way Brewster, MA 02631 119 1-F Yes PB 6000 X
7/11/23Spoke with J. Packett Golf
Dir.,requested bid from operator,
price for 4x inspections $8600 +/-.
Consulting with Town Admin. office
for combining town properties for
inspections.
17 Granite State Court Cape Associates Inc. PO Box 1858 North Eastham, MA 02651 138 47 No BR 2140 8/24/2023 X
9/14/23 Title 5 Report needs pressure
distribution information. Spoke w/
inspector
18 199 Hamilton Cartway Sandra Nayak, Trustee of The Nayak Brewster Realty Trust 12 Orchard Street Belmont, MA 02478 93 3 No BR 266.4 X
19 283 Hamilton Cartway Kelly Mobley, Trustee of Kolb Properties Realty Trust 1611 Whitman Drive West Melbourne, FL 32904 81 1 Yes HR 330
New 2023 to be installed - PercRite
System
20 62 Harvest Lane Carl Firlings Et AL 9 Jib Court Middletown, RI 02842 68 66 No CCB 475.95 X
21 Huckleberry Lane System 1 Brewster Housing Authority 11 Frederick Court Brewster, MA 02631 142 6 No PB 3813
11/13/23Email from Chad, Coastal
Eng. requesting clarification on
frequency of mandatory inspections
22 Huckleberry Lane System 2 Brewster Housing Authority 11 Frederick Court Brewster, MA 02631 142 6 No PB 3740
11/13/23Email from Chad, Coastal
Eng. requesting clarification on
frequency of mandatory inspections
23 54 John Wings Lane Stuart Koman C/O The Stuart Koman Trustee 54 John Wings Lane Brewster, MA 02631 23 47 No CCB 503 X
24 72 Johnson Cartway Bruce & Nancy Johnson 72 Johnson Cartway Brewster, MA 02631 61 21 No HR 330 12/1/2022 11/30/2021 Perc-Rite System
25 75 Johnson Cartway Craig & Carolyn Colgate PO Box 1841 Brewster, MA 02631 61 20 No HR 440 12/1/2022 11/24/2021 12/10/2020 12/20/2019 Perc-Rite System
26 42 Konohassett Cartway Joseph Carty & Diana Pohly 42 Konohassett Cartway Brewster, MA 02631 72 25 10/18/2022 X
27 200 Lower Road Jake V. & Nancy A. Drake, Trustees Brier Lane Nominee Trust P.O. Box 935 Brewster, MA 02631 48 45 No CCB 474 3/20/2020 12/10/2020 10/3/2022 Perc-Rite System
28 0 Main Street Eastward MBT, LLC Trustee 155 Crowell Road Chatham, MA 02633 139 74 No NC 452 New System to be installed
29 89 Main Street Xiaobei Sullivan 89 Main Street Brewster, MA 02631 6 13 No QC 578 X
Response letter received 7/26/23,
system pumped only
30 523 Main Street Hilary & Steven Hickok, The Hilary Hickok Trust 523 Main Street Brewster, MA 02631 16 21 No QC 331.7 X
31 1646 Main Street Latham Centers Inc. 1646 Main Street Brewster, MA 02631 56 69 No CCB 1100 X
32 1990 Main Street Westerly Holdings LLC PO Box 2000 Brewster, MA 02631 67 97 No QC 210 X
33 2639 Main Street Brewster Main Street Realty Trust PO Box 524 South Yarmouth, MA 02664 89 18 No CCB 1709 X
34 2553 Main Street Michele Rowan PO Box 1026 Brewster, MA 02631 78 76 No CCB 793.3 X New system installed 11/17/23
35 3057 Main Street (2005 CC Sea Camps)Town of Brewster 2198 Main Street Brewster, MA 02631 101 45 No CCB 555 X
MA DEP Groundwater Discharge
Permit/5 year inspection cycle.
36 3057 Main Street (2009 CC Sea Camps)Town of Brewster 2198 Main Street Brewster, MA 02631 101 45 No CCB 555 X
MA DEP Groundwater Discharge
Permit/5 year inspection schedule.
37 2639 Main Street (Cumberland Farms)Brewster Main Street Realty Trust PO Box 524 South Yarmouth, MA 02664 89 18 No CCB 474 X
Recv'd letter from owner on 7.26.23.
Repair work completed to replace
failed pump.
N:\Health\Pressure Dosing\Pressure Dose Systems - Brewster MA 12.28.2023
Brewster Pressure Dose Systems
12/28/2023
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A B C D E F G H I J K L M N O P Q
38 2298 Main Street (Eddy Elementary School)Town of Brewster 2298 Main Street Brewster, MA 02631 77 58 No CCB 6660 7/14/2023 3/20/2023 X
7/14/23,8/29/23,9/8/23 emails from
D. Caolo-Eddy School requested O &
M Operator Coastal Eng. for proposal.
Need to locate system and build up
laterals to inspect. Waiting for cost
estimate. 11/21/23D.Caolo sent
request to management for
permission to solicit quotes due to
expense of repairs and inspections.
39 1671 Main Street (Fire Station)Town of Brewster 1671 Main Street Brewster, MA 02631 56 6 No CCB 2533 X
8/14/23,8/17/23 Emails from K.Varley
requested proposal from system
inspector, consulting with Town
Admin. Re: one contractor for all
town properties 11/21/23 FD
soliticing other inspection quotes.
40 1993 Main Street (The Brewster Inn)Andrew Murphy, Trustee, The Main Street Realty Trust PO Box 773 East Dennis, MA 02641 67 2 No CCB 2690 X
41 3260 Main Street 1&2 (Cobies)Robert Slavin, Trustee, Roberts Realty Trust 3238 Main Street Brewster, MA 02631 101 47 No CCB 2710 Inspection to be done at end of Aug '23 X
Inspection scheduled for end of Aug.
12/26/23 No inspection to date.
42 80 Mill Pond Drive Carmine & Krista Cutone 80 Mill Pond Drive Brewster, MA 02631 34 48 No CCB 338 X
43 26 Nancy May Path David A. Gillespie & Susan T Sabetti, Trustees, Gilsab Joint Trust 47 Tucker Ridge Court Hilton Head, SC 29926 91 14-801 No CCB 330 12/6/2022 11/24/2021 12/9/2020 12/2022019 Perc-Rite System
44 119 North Pond Drive Calvin & Karen Mutti 119 North Pond Drive Brewster, MA 02631 89 61 No CCB 337 X
45 85 Olde Owl Pond Road Ralph & Katherine Tupper; Steven & Stephanie Tupper 105 Olde Owl Pond Road Brewster, MA 02631 137 75 No NC 440 Perc-Rite System
46 254 Robbins Hill Road Evelyn Maguire Trustee, Evelym B. Maguire Trust C/O Carolyn Shea 22 Cross Street Harwichport, MA 02646 38 84 No CCB 475 8/16/2023 X
47 255 Robbins Hill Road Howard Hayes, Trustee Corcoran Nominee Trust PO Box 1048 Brewster, MA 02631 38 58 No CCB 586 12/6/2022 12/21/2021 12/14/2020 10/16/2023 X Perc-Rite System
48 371 Robbins Hill Road 371 Robbins Hill Road LLC C/O Robbins Hill Creek LLC 770 Boylston Street, Penthouse 27D Boston, MA 02199 38 73 No CCB 471 X
49 242 Seaway Road Sean & Nicole Cronican 211 Marsh Street Belmont, MA 02478 79 110 No CCB 444 X
50 53 Sheep Pond Circle Marjorie Smeltzer 820 Harwich Road Apt 171 Brewster, MA 02631 73 11 No HR 451 X
51 42 Six Penny Lane David Howland & Erika Holzbaur-Howland 2408 Waverly Street Philadelphia, PA 19146 37 29 No CCB 334 4/29/2019 2/15/2008 X
52 56 Six Penny Lane Eunice Terrenzi 56 Six Penny Lane Brewster, MA 02631 37 27 No CCB 335 X
53 0 South Orleans Road(White Rock Commons)White Rock Homeowners Association 35 Beacon Hill Way South Chatham, MA 02659 130 34 No PB 4070 10/2/2022 6/20/2022 3/22/2022 12/16/2022 X(sent back 7.26.23 wrong address Letter resent 7.26.23
54 100-120 Southern Eagle Cartway Christopher & Clinton Kanaga Trustees, HKN Trust PO Box 236 Orleans, MA 02653 138 43 No BR 675 X
55 842 Stony Brook Road Gino Verzone 842 Stony Brook Road Brewster, MA 02631 35 46 No CCB 553.52 3/18/2014 1/17/2008 6/8/2007 X
56 468 Stony Brook Road (Our Lady of the Cape Church)Roman Catholic Bishop, Our Lady of the Cape PO Box 1799 Brewster, MA 02631 25 3 No QC 3450 X
57 102 Susan Lane Sean Bennett 102 Susan Lane Brewster, MA 02631 55 4 No CCB 332 X
58 57 The Channel Way Martha Dunbar, Trustee 54 Haven Street Milford, MA 01757 58 5 No CCB 555 X
59 90 The Channel Way Estate of John Henry, Nancy Asfour, Personal Representative 90 The Channel Way Brewster, MA 02631 58 74 No CCB 566 X
60 93 The Channel Way William Glynn & Ann Lombroso, Trustees 64 Birchwood Lane Lincoln, MA 01773 58 6 No CCB 444 X
61 42 Warrens Road Pamela Lloyd-Baker 45 Warrens Road Brewster, MA 02631 38 99 No CCB 330 12/6/2022 11/24/2021 11/26/2019 10/11/2018 Perc-Rite System
Letter sent w/ response
Compliant
N:\Health\Pressure Dosing\Pressure Dose Systems - Brewster MA 12.28.2023
KEY: Red => 19 ppm TN Brewster I/A Systems Per County Database
10/11/2021-12/26/2023
Permit Number Site Address Sample Date Operator Component
Effluent Total
Nitrogen
Effluent
Nitrate
Effluent
Nitrite
Efflu.Total
Kjehldahl
Nitrogen
Effluent
BOD, 5-Day
Effluent Total
Suspended
Solids
Effluent
Total
Phosphorus
Effluent Total Dissolved
Phosphorus
1 BREW-Wil120-ADV 120 William Maker Way 2023-06-14 J.M. O'Reilly Advantex 1.19 0.19 1 2.7 2
2 BREW-Bea127-Bio 127 Beach Plum Lane 2022-03-08 Coastal Bioclere 19.2 18 1.2 97
3 BREW-Bea127-Bio 127 Beach Plum Lane 2022-03-08 Coastal Bioclere 19.2 18 1.2 97
4 BREW-Bea127-Bio 127 Beach Plum Lane 2022-09-21 Coastal Bioclere 2.21 0.89 1.32
5 BREW-Bea127-Bio 127 Beach Plum Lane 2023-03-06 Coastal Bioclere 14.88 11 0.65 3.23 7.2
6 BREW-Sou157-Sep 157 South Orleans Road 2021-11-29 J.M. O'Reilly Septitech 12.04 9.5 0.34 2.2 5 3.6
7 BREW-Sou157-Sep 157 South Orleans Road 2022-02-23 J.M. O'Reilly Septitech 16.58 14 0.28 2.3 3.6
8 BREW-Sou157-Sep 157 South Orleans Road 2022-05-23 J.M. O'Reilly Septitech 13.22 9.1 0.42 3.7 7.4 2.4
9 BREW-Sou157-Sep 157 South Orleans Road 2022-09-01 J.M. O'Reilly Septitech 9.33 6.9 0.43 2 3.1 3.2
10 BREW-Sou157-Sep 157 South Orleans Road 2022-11-22 J.M. O'Reilly Septitech 11.83 9.5 0.23 2.1 6.4
11 BREW-Sou157-Sep 157 South Orleans Road 2023-03-22 J.M. O'Reilly Septitech 75.9 6.6 1.3 68 6 39
12 BREW-Sou157-Sep 157 South Orleans Road 2023-06-14 J.M. O'Reilly Septitech 12.47 9.9 0.37 2.2 3.6
13 BREW-Sou157-Sep 157 South Orleans Road 2023-08-25 J.M. O'Reilly Septitech 11.1 10 1.1 2.8
14 BREW-Jon158-Sin 158 Jonathans Way 2022-01-05 Siegmund Singulair 9.9 9.9
15 BREW-Jon158-Sin 158 Jonathans Way 2022-03-23 Siegmund Singulair 17 17
16 BREW-Jon158-Sin 158 Jonathans Way 2022-11-17 Siegmund Singulair 67.6 27 1.4 39.2
17 BREW-Jon158-Sin 158 Jonathans Way 2023-03-16 Siegmund Singulair 62 0.15 61.7
18 BREW-Jon158-Sin 158 Jonathans Way 2023-03-23 Siegmund Singulair 21 17 4.07
19 BREW-Jon158-Sin 158 Jonathans Way 2023-06-15 Siegmund Singulair 47 0.055 47
20 BREW-Jon158-Sin 158 Jonathans Way 2023-08-31 Siegmund Singulair 2.2 0.7 1.5
21 BREW-Jon158-Sin 158 Jonathans Way 2023-10-25 Siegmund Singulair 15 2.8 3.5 9.11
22 BREW-Lon159-Bio 1597 Long Pond Road 2022-01-10 Bennett Bioclere 7.3 5.9 1.4 21
23 BREW-Lon159-Bio 1597 Long Pond Road 2022-07-25 Bennett Bioclere 79.77 46 0.079 33.7 220
24 BREW-Lon159-Bio 1597 Long Pond Road 2023-01-17 Bennett Bioclere 34 34 7.8
25 BREW-Lon159-Bio 1597 Long Pond Road 2023-07-06 Bennett Bioclere 8.724 7.7 0.091 0.933 10
26 BREW-Rus017-Wat 17 Russells Path 2021-11-01 Bennett Waterloo 9.43 6.9 2.53 4.1
27 BREW-Rus017-Wat 17 Russells Path 2022-04-13 Bennett Waterloo 16.42 4.3 0.42 11.7 7.1
28 BREW-Rus017-Wat 17 Russells Path 2022-10-17 Bennett Waterloo 9.988 7.7 0.068 2.22 5.5
29 BREW-Rus017-Wat 17 Russells Path 2023-04-27 Bennett Waterloo 8.47 6.7 1.77
30 BREW-Rus017-Wat 17 Russells Path 2023-04-27 Bennett Waterloo 8.47 6.7 1.77
31 BREW-Rus017-Wat 17 Russells Path 2023-10-24 Bennett Waterloo 5.79 3.3 2.49 9.3
32 BREW-Bur019-Bio 19 Burning Bush Way 2022-03-09 Coastal Bioclere 19.75 19 0.35 0.4 2.2 8.7
33 BREW-Bur019-Bio 19 Burning Bush Way 2022-03-09 Coastal Bioclere 19.75 19 0.35 0.4 2.2 8.7
34 BREW-Bur019-Bio 19 Burning Bush Way 2023-03-09 Coastal Bioclere 9.17 5.4 0.16 3.61 2.9
35 BREW-Bri200-FAS 200 Brier Lane 2022-09-01 J.M. O'Reilly FAST 12.31 9.6 0.31 2.4 31 14
36 BREW-Rob298-Adv 298 Robbins Hill Road 2021-11-01 Bennett Advantex 84.3 66 18.3 10
37 BREW-Rob298-Adv 298 Robbins Hill Road 2022-05-27 Bennett Advantex 5.612 5.2 0.098 0.314
38 BREW-Rob298-Adv 298 Robbins Hill Road 2023-05-04 Bennett Advantex 106 88 18
39 BREW-Rob298-Adv 298 Robbins Hill Road 2023-10-25 Bennett Advantex 90.93 82 8.93
40 BREW-Bre030-BIO 30-40 Brewster Woods Drive2023-04-28 Coastal Bioclere
41 BREW-Bre030-BIO 30-40 Brewster Woods Drive2023-10-20 Coastal Bioclere 26 46
42 BREW-Sat320-Sin 320 Satucket Road 2021-11-01 Bennett Singulair 51.6 51.6 47 120
43 BREW-Sat320-Sin 320 Satucket Road 2022-01-20 Bennett Singulair 44.3 44.3 86 140
44 BREW-Sat320-Sin 320 Satucket Road 2022-04-13 Bennett Singulair 61.8 61.8 70 150
45 BREW-Sat320-Sin 320 Satucket Road 2022-10-17 Bennett Singulair 72.47 0.33 0.24 71.9 140 140
46 BREW-Sat320-Sin 320 Satucket Road 2023-01-17 Bennett Singulair 69.573 0.1 0.073 69.4 150 230
47 BREW-Sat320-Sin 320 Satucket Road 2023-07-07 Bennett Singulair 56.312 0.12 0.092 56.1 49 240
48 BREW-Sat320-Sin 320 Satucket Road 2023-08-31 Siegmund Singulair 58.616 0.13 0.086 58.4 59 160
49 BREW-McG039-FAS 39 McGuerty Road 2021-11-30 J.M. O'Reilly FAST 27.51 19 0.41 8.1 9
50 BREW-McG039-FAS 39 McGuerty Road 2022-03-09 J.M. O'Reilly FAST 51.54 6.3 0.24 45 0 11
51 BREW-McG039-FAS 39 McGuerty Road 2022-05-23 J.M. O'Reilly FAST 40.95 17 0.95 23 35 31
52 BREW-McG039-FAS 39 McGuerty Road 2022-09-01 J.M. O'Reilly FAST 20.39 12 0.79 7.6 13
53 BREW-McG039-FAS 39 McGuerty Road 2022-11-22 J.M. O'Reilly FAST 38.21 6.8 0.41 31 25 17
N:\Health\IA Information\BOH IA Enforcement Information\Brewster IA Systems Spreadsheet County Data 12.26.2023
KEY: Red => 19 ppm TN Brewster I/A Systems Per County Database
10/11/2021-12/26/2023
Permit Number Site Address Sample Date Operator Component
Effluent Total
Nitrogen
Effluent
Nitrate
Effluent
Nitrite
Efflu.Total
Kjehldahl
Nitrogen
Effluent
BOD, 5-Day
Effluent Total
Suspended
Solids
Effluent
Total
Phosphorus
Effluent Total Dissolved
Phosphorus
54 BREW-McG039-FAS 39 McGuerty Road 2023-05-17 J.M. O'Reilly FAST 22.39 14 0.69 7.7 15 15
55 BREW-McG039-FAS 39 McGuerty Road 2023-08-28 J.M. O'Reilly FAST 37 23 14 18 20
56 BREW-Cra040-Wat 40 Cranview Road 2021-11-15 BCDHE Waterloo EC-P 3.1 1.5
57 BREW-Cra040-Wat 40 Cranview Road 2021-11-15 BCDHE Pump Chamber 58 8.6 8
58 BREW-Cra040-Wat 40 Cranview Road 2022-03-23 BCDHE Pump Chamber 58 6.61 6.02
59 BREW-Cra040-Wat 40 Cranview Road 2022-03-23 BCDHE Waterloo EC-P 19 18.7 3.38
60 BREW-Cra040-Wat 40 Cranview Road 2022-05-18 BCDHE Waterloo EC-P 8 4.31 3.35
61 BREW-Cra040-Wat 40 Cranview Road 2022-05-18 BCDHE Pump Chamber 56 7.45 7.03
62 BREW-Cra040-Wat 40 Cranview Road 2022-11-07 BCDHE Waterloo EC-P 5 28.1 28.1
63 BREW-Cra040-Wat 40 Cranview Road 2023-06-15 BCDHE Waterloo EC-P 7.8
64 BREW-Com044-FAS 44 Commons Way 2023-05-17 WTS FAST 22.78 18.9 3.88
65 BREW-Com044-FAS 44 Commons Way 2023-08-17 WTS FAST 9.96 7.51 0.72 1.73
66 BREW-Com044-FAS 44 Commons Way 2023-10-26 WTS FAST 8.2 3.09 5.11
67 BREW-Sar050-FAS 50 Sarah Maker Lane 2021-12-07 WTS FAST 14.33 13.4 0 0.93
68 BREW-Sar050-FAS 50 Sarah Maker Lane 2022-03-29 WTS FAST 30.25 9.85 0 20.4
69 BREW-Sar050-FAS 50 Sarah Maker Lane 2022-10-18 WTS FAST 47.66 8.36 0 39.3
70 BREW-Sar050-FAS 50 Sarah Maker Lane 2023-02-17 WTS FAST 28.9 11.9 0 17
71 BREW-Sar050-FAS 50 Sarah Maker Lane 2023-08-17 WTS FAST 32.36 3.96 0 28.4
72 BREW-Sea050-Sep 50 Sea Meadow Lane 2021-12-07 WTS Septitech 12.45 11 1.45
73 BREW-Sea050-Sep 50 Sea Meadow Lane 2022-02-08 WTS Septitech 9.03 7.3 1.73
74 BREW-Sea050-Sep 50 Sea Meadow Lane 2022-06-14 WTS Septitech 13.91 11.6 2.31 4.4
75 BREW-Sea050-Sep 50 Sea Meadow Lane 2022-09-14 WTS Septitech 15.4 15.4
76 BREW-Sea050-Sep 50 Sea Meadow Lane 2022-10-18 WTS Septitech 11.42 8.52 2.9
77 BREW-Sea050-Sep 50 Sea Meadow Lane 2022-12-21 WTS Septitech 9.07 7 2.07 5.7
78 BREW-Sea050-Sep 50 Sea Meadow Lane 2023-02-17 WTS Septitech 5.77 3.98 1.79 4.5 10.5
79 BREW-Sea050-Sep 50 Sea Meadow Lane 2023-05-17 WTS Septitech 13.8 13.8 6.9 10.5
80 BREW-Sea050-Sep 50 Sea Meadow Lane 2023-10-26 WTS Septitech 5.62 5.62 11.5 7
81 BREW-Thou054-FAS 54 Thousand Oaks Drive 2022-03-29 WTS FAST 35.81 13.2 17.7 4.91
82 BREW-Thou054-FAS 54 Thousand Oaks Drive 2022-07-08 WTS FAST 13.68 10.9 2.78
83 BREW-Thou054-FAS 54 Thousand Oaks Drive 2023-03-14 WTS FAST 29.94 29.1 0.84
84 BREW-Thou054-FAS 54 Thousand Oaks Drive 2023-08-17 WTS FAST 16.4 16.4
85 BREW-McG056-Sin 56 McGuerty Road 2021-11-01 Bennett Singulair 33.8 2.4 8.4 23 51 62
86 BREW-McG056-Sin 56 McGuerty Road 2022-10-17 Bennett Singulair 97.64 0.24 1.3 96.1 170 490
87 BREW-Tho007-Adv 7 Thousand Oaks Drive 2021-11-30 J.M. O'Reilly Advantex 31.98 22 0.28 9.7 46
88 BREW-Tho007-Adv 7 Thousand Oaks Drive 2022-02-23 J.M. O'Reilly Advantex 28.8 21 0.1 7.7 58
89 BREW-Old078-Sin 78 Old Red Top Road 2022-04-26 Siegmund Singulair 6.09 3.2 0.23 2.66 19 6.5
90 BREW-Old078-Sin 78 Old Red Top Road 2022-11-17 Siegmund Singulair 28.64 0.33 0.21 28.1 22 7.4
91 BREW-Old078-Sin 78 Old Red Top Road 2023-05-22 Siegmund Singulair 37 12 6.6 18.4 110 62
92 BREW-Gre083-FAS 83 Greenland Pond Road 2021-12-09 WTS FAST 35.26 13.7 1.76 19.8
93 BREW-Gre083-FAS 83 Greenland Pond Road 2022-03-29 WTS FAST 37.8 17.6 20.2
94 BREW-Gre083-FAS 83 Greenland Pond Road 2022-06-14 WTS FAST 33.78 25.5 8.28
95 BREW-Gre083-FAS 83 Greenland Pond Road 2022-10-18 WTS FAST 70 18 52
Enforce. Letter Sent w/ response
Enforce. Letter Sent no response
BOH to review
N:\Health\IA Information\BOH IA Enforcement Information\Brewster IA Systems Spreadsheet County Data 12.26.2023
12/28/2023 Brewster I/A Systems
Number Street Map/Parcel Brand DEP Approval Year Nutrient Reduction Nutr. Limit ESA O&M Contract Compliance Notification Response
1 127 Beach Plum Lane 96/63 Bioclere Provisional Y
2 306 Blueberry Pond Drive 101/100 Presby General
2013 BOH and DEP d/c
Inspection rqrmnt
3 30 Brewster Woods Road 56/75 Bioclere General 2021
>2000gpd - Ch. 40B development
exempt Y Y
4 200 Brier Lane 48/45 Perc-Rite Remedial
5 19 Burning Bush Way 33/267 Bioclere Provisional
6 34 Captain Connolly Road 19/29 Perc-Rite General
historically non-
compliant
10/2021 BOH
hearing
7 5 Carson's Way 23/60 Micro Fast 0.9 General
8 47 Carson's Way 23/63 H600A H-Series Hoot
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
9 60 Carson's Way 23/64 Micro Fast 0.9 General
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
10 56 Carson's Way 23/65 Micro Fast 0.9 General
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
11 14 Carson's Way 23/67 Micro Fast 0.5 General
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
12 26 Carson's Way 23/68 Micro Fast 0.5L General
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
13 35 Carson's Way 23/62 Micro Fast 0.5 General
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
14 40 Carson's Way 23/66 Micro Fast 0.5 General
Water Quality Reg (Zoning) - 4 or
more dwellings d/c > 2000 gpd Y
15 19 Cedar Hill Road 38/20 Perc-Rite
16 44 Commons Way 97/93 MicroFAST 0.5 General 2022 Nitrogen 19 ppm Zone II/DCPC/CC Bay Watershed Y Y 10/18/23 Monitor for 1 year per BOH 10/18/23
17 40 Cranview 38/74 Waterloo Biofilter Pilot 2018 Phosphorous 300' Elbow Pond, Bog, GW@ 4.5'County No
18 300 Foster Road 79/25 Micro Fast 0.5 General N No Letter 6/30/23
19 83 Greenland Pond Road 94/27 MicroFAST 0.5 General 2021 Nitrogen 19 ppm
Zone II/DCPC/Herring River
Watershed N No Letter 9/27/23
9/27/23 Cert. mail returned-unable to find correct mailing address.
10/24/23 Letter resent & no response.
20 75 Johnson Cartway 61/20 Perc-Rite General
21 158 Jonathan's Way 95/7 Singulair General w/ N Letter 8/22/23
22 85 Hamilton Cartway 93/9 Advantex A20
23 88 Hamilton Cartway 93/11 Micro Fast / Drip Dispersal
24 283 Hamilton Cartway 81/1 PercRite Drip Dispersal General 2023
Zone II/300' to Greenland & Long
Ponds/ESA/Herring River
Watershed New Installation 2023
25 40 Konohassett Cartway 72/25 Micro Fast 0.5 General
26 495 Long Pond Road 85/111 Septi-tech General
27 1597 Long Pond Road 94/93 Bioclere Provisional 2003 Nitrogen 19 ppm
Zone II/DCPC/Herring River
Watershed Y Y Letter 8/22/23 NSU/Owner 9/11/23. Monitor for 1 year per BOH 9/20/23
28 15 Lower Road 37/1 Micro Fast 4.5 General 2006 Nitrogen 25 ppm
300' to saltmarsh/test every 3
years/CC Bay Wtshed Y No
29 540 Main Street 26/7 Micro Fast w/ UV General w/ N
30 2907 Main Street (Ocean Edge)Amphidrome Pilot
31 54 Mate's Way 18/32 Sludge Hammer
32 39 McGuerty Road 94/75 Micro Fast 0.5 General 2018 Nitrogen 19 or 25 ppmZone II/DCPC not addressed Y No Letter 8/22/23
JMO'Reilly Email 9/1/23 Influent test scheduled. 12/27/23 Email sent
to operator for update on influent test.12/28/23 December
effluent/influent samples completed & waiting for results.
33 56 McGuerty Road 94/88 Singulair Pilot 2002 Nitrogen Zone II/DEP reduct. approv. 1x/year Y No Letter 8/22/23
9/11/21 NSU contract prop.9/21/23 NSU reminder to owner
contract prop.9/25/23 NSU email to owner/BOH re: extension
request to pump system then test-ok.12/27/23 Email sent to
operator for update.
34 26 Nancy May Path 91/14-801 Perc Rite
35 78 Old Red Top Road 12/72 Singulair Remedial w/ N Ck on 8/16/24 8/16/23 HOLD - review in 1 year
N:\Health\IA Information\BOH IA Enforcement Information\Brewster IA Systems Spreadsheet MASTER 2023
12/28/2023 Brewster I/A Systems
36 160 Old Red Top Road 12/44 Singulair Pilot/General2019 2003 Nitrogen 25 ppm Zone II/DCPC/CC Bay Watershed Y Y Letter 6/28/23 10/2/23 Contract w/ Bennett,sample start 2/24
37 85 Old Owl Pond Road 137/75 Perc Rite
38 65 Pell's Fishing Road 125/50 White Knight
39 255 Robbin's Hill Road 38/58 Perc Rite
40 298 Robbin's Hill Road 38/80 Advantex AX25RT Remedial w/ N 2020 Nitrogen 19 ppm 300' to wetland/CC Bay Watershed Y No Letter 10/25/23 No response from owner.
41 17 Russell's Path 85/73 Waterloo Biofilter Provisional 2005 Nitrogen Zone II Yes Yes
42 0 Sachemus Trail 78/Bioclere w/ Cultex LF General
43 50 Sarah Maker Lane 85/138 Micro Fast General 2014 Nitrogen 19 ppm
Zone II/DCPC/Herr. River & CC Bay
Wtshed/Priv.Well N No Letter 9/27/23
10/3/23 Call from owner. Returned call - unable to leave
message.10/16/23 Spoke w/ owner.Will contact Wastewater
Services and advise.011/9/23 Owner advised by operator of
recommendations to reduce TN.
44 18 Samoset Road 85/134 Micro Fast
45 120 Satucket Road 13/103 Singulair 960 NR
46 320 Satucket Road 13/103 Singulair 960 NR Provisional 2007 Nitrogen 19 ppm Zone II/DCPC/CC Bay Watershed Y No Letter 8/22/23
9/1/23 New O&M Contract w/ Siegmund Env. Last test 8/31/23. New
samples late, system noncompliant.
47 50 Sea Meadow Lane 37/71 Micro Fast
48 6 Seaman's Lane 12/71 Micro Fast 0.5
49 53 Sheep Pond Circle 73/11 Biotube ProPak Pump
50 42 Six Penny Lane 37/29 Micro Fast Remedial
51 157 South Orleans Road 142/102 Septi-tech M3000N
52 842 Stony Brook Road 35/46 Micro Fast Remedial
53 75 Swift Lane Sludge Hammer
54 7 Thousand Oaks Drive 107/21 Advantex Provisional Nitrogen Zone II No No Letter 8/22/23
9/7/23 Owner contacted office.9/21/23 Owner update - waiting for
response from operator.10/4/23 Owner update-JM O'Reilly
responded no but will reassess.11/23 Owner contacted Health Dept.
unable to find operator on Cape. Advised may need to hire off-Cape
operator until owner can contract with local operator.
55 54 Thousand Oaks Drive 108/23 Micro Fast General 2016 Nitrogen 19 ppm
Zone II/DCPC/Pleasant Bay
Watershed Y No Letter 9/27/23 10/13/23 No response
56 Trevor Lane (Ocean Edge)White Knight
57 42 Warren's Road 38/75 Perc Rite
58 120 Woodlands Lane (PBA Living)143/12 Amphidrome
Pending Review in 1 year
N:\Health\IA Information\BOH IA Enforcement Information\Brewster IA Systems Spreadsheet MASTER 2023
Massachusetts Department of Environmental Protection
eDEP Transaction Copy
Here is the file you requested for your records.
To retain a copy of this file you must save and/or print.
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Document:
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Status of Transaction:
Date and Time Created:
Note: This file only includes forms that were part of your
transaction as of the date and time indicated above. If you need
a more current copy of your transaction, return to eDEP and
select to “Download a Copy” from the Current Submittals page.
1649110
12/12/2023:1:31:21 PM
1081.41K
SFARRENKOPF
Groundwater Discharge Monitoring Report Forms
In Process
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
PLEASANT BAY HEALTH CTR
a. Name
383 SOUTH ORLEANS ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
JOSEPH SMITH
a. Name of Facility Contact Person
7742125005 jsmith@nsuwater.com
b. Telephone Number c. email address
3. Sampling information:
11/1/2023 NOT APPLICABLE
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
BEA/NSU WWTO PERSONNEL
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Daily Log Sheet 2023 Nov Daily
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DAILY LOG SHEET
746
1. Permit Number
200303120
2. Tax identification Number
2023 NOV DAILY
3. Sampling Month & Frequency
C. Daily Readings/Analysis Information
Date Effluent
Flow GPD
Reuse
Flow GPD
Irrigation
Flow GPD
Turbidity Influent pH Effluent
pH
Chlorine
Residual
(mg/l)
UV
Intensity
(%)
1 11144 6.9 88.6
2 12391 6.7 95
3 12206 6.6 85.7
4 12206
5 12206
6 13002 6.5
7 9449 6.5
8 10562 6.5 33
9 10422 6.7 33.3
10 12265 6.7 28.6
11 12265
12 12265
13 12879 6.7 29
14 7385 6.8 72.9
15 11743 6.8 28.1
16 6681 6.9 6.9 72.9
17 9859 6.8 24.2
18 9859
19 9859
20 6930 7.1 18.8
21 13585 6.6 18.7
22 9734 6.8 17.2
23 9734
24 9734
25 9734
26 9734
27 14001 6.5 73.6
28 6752 6.8 73.6
29 8890 6.8 12.8
30 6619 7.0 12.4
31
gdpdls.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DAILY LOG SHEET
746
1. Permit Number
200303120
2. Tax identification Number
2023 NOV DAILY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
PLEASANT BAY HEALTH CTR
a. Name
383 SOUTH ORLEANS ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
JOSEPH SMITH
a. Name of Facility Contact Person
7742125005 jsmith@nsuwater.com
b. Telephone Number c. email address
3. Sampling information:
11/2/2023 ALPHA ANALYTICAL
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
ALPHA ANALYTICAL PERSONNEL
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Discharge Monitoring Report 2023 Nov Monthly
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DISCHARGE MONITORING REPORT
746
1. Permit Number
200303120
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
D. Contaminant Analysis Information
For "0", below detection limit, less than (<) value, or not detected, enter "ND"
TNTC = too numerous to count. (Fecal results only)
NS = Not Sampled
1. Parameter/Contaminant 2. Influent 3. Effluent 4. Effluent Method
Units Detection limit
BOD 130 ND 2.0
MG/L
TSS 83 ND 5.0
MG/L
TOTAL SOLIDS 300 240 13
MG/L
AMMONIAN 16.2
MG/L
NITRATEN 0.90 0.10
MG/L
TOTAL NITROGEN(NO3+NO2+TKN)1.62 0.450
MG/L
OIL & GREASE ND 3.6
MG/L
FECAL COLIFORM ND 2.0
/100 ML
CHLORIDE 48 1.0
MG/L
infeffrpblank.doc • rev. 09/15/15 Groundwater Permit Discharge Monitoring Report • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DISCHARGE MONITORING REPORT
746
1. Permit Number
200303120
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
PLEASANT BAY HEALTH CTR
a. Name
383 SOUTH ORLEANS ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
JOSEPH SMITH
a. Name of Facility Contact Person
7742125005 jsmith@nsuwater.com
b. Telephone Number c. email address
3. Sampling information:
11/29/2023 NOT APPLICABLE
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
BEA/NSU WWTO PERSONNEL
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Monitoring Well Data Report 2023 Nov Monthly
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
MONITORING WELL DATA REPORT
746
1. Permit Number
200303120
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
C. Contaminant Analysis Information
For "0", below detection limit, less than (<) value, or not detected, enter "ND"
TNTC = too numerous to count. (Fecal results only)
NS = Not Sampled
DRY = Not enough water in well to sample.
<
Parameter/Contaminant DG1 DG2 DG4 UG1
Units Well #: 1 Well #: 2 Well #: 3 Well #: 4 Well #: 5 Well #: 6
PH 5.47 6.15 6.63 6.45
S.U.
STATIC WATER LEVEL 10.76 10.82 10.74 11.01
FEET
SPECIFIC CONDUCTANCE 281 342 355 169
UMHOS/C
mwdgwpblank.doc • rev. 09/15/15 Monitoring Well Data for Groundwater Permit • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
MONITORING WELL DATA REPORT
746
1. Permit Number
200303120
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
Any person signing
a document under
314 CMR 5.14(1) or
(2) shall make the
following
certification
If you are filing
electronically and
want to attach
additional
comments, select
the check box.
Facility Information
PLEASANT BAY HEALTH CTR
a. Name
383 SOUTH ORLEANS ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
Certification
“I certify under penalty of law that this document and all attachments were prepared under my direction or supervision in
accordance with a system designed to assure that qualified personnel properly gather and evaluate the information submitted.
Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate and complete. I am aware that there
are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations.”
SAMANTHA FARRENKOPF 12/12/2023
a. Signature b. Date (mm/dd/yyyy)
Reporting Package Comments
BENNETT ENVIRONMENTAL ASSOCIATES, LLC. (BEA) HAS COMPLETED THE NOVEMBER
2023 MONTHLY INFLUENT AND EFFLUENT SAMPLING OF THE AMPHIDROME WASTEWATER
TREATMENT SYSTEM. MONTHLY WASTEWATER SAMPLING WAS COMPLETED ON 11/2/23.
LABORATORY RESULTS REPORTED ALL PARAMETERS WITHIN DISCHARGE PERMIT
LIMITATIONS. EFFLUENT PH WAS REPORTED WITHIN THE 6.58.5 RANGE THROUGHOUT THE
MONTH. FLOW VOLUME MEASUREMENTS WERE ASSESSED DURING THE MONTH FROM
THE SYSTEM’S EFFLUENT FLOW METER. DAILY FLOW REMAINED WITHIN THE 26,500GPD
LIMITATION THROUGHOUT THE MONTH. THE MINIMUM, MAXIMUM AND AVERAGE GPD
FLOWS REPORTED OVER THE COURSE OF THE MONTH WERE 6,619 GPD, 14,001 GPD AND
10,470 GPD, RESPECTIVELY.
DURING THE COURSE OF THE MONTH, THE UV METER PERIODICALLY DIDN’T DISPLAY THE
UV PERCENTAGE READING DUE TO A REOCCURRING NUISANCE ALARM. AS SUCH, UV
INTENSITY IS REPORTED IN W/M2 UNITS FOR THE FOLLOWING DAYS: NOVEMBER 6TH –
13TH, NOVEMBER 16, NOVEMBER 20TH – 22ND, NOVEMBER 29TH, AND NOVEMBER 30TH,
2023. BEA IS WORKING WITH THE UV SYSTEM MANUFACTURER TO DIAGNOSE AND
RESOLVE THE NUISANCE ALARM.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
746
1. Permit Number
200303120
2. Tax identification Number
L2365178
Bennett Environmental Associates
K47810DA.S.WW.700
PLEASANT BAY
Client:
Project Name:
Project Number:
11/13/23
Eight Walkup Drive, Westborough, MA 01581-1019
Lab Number:
Report Date:
508-898-9220 (Fax) 508-898-9193 800-624-9220 - www.alphalab.com
1573 Main Street
Brewster, MA 02631
Joseph SmithATTN:
ANALYTICAL REPORT
Certifications & Approvals: MA (M-MA086), NH NELAP (2064), CT (PH-0826), IL (200077), IN (C-MA-03), KY (KY98045), ME (MA00086), MD
(348), NJ (MA935), NY (11148), NC (25700/666), OH (CL108), OR (MA-1316), PA (68-03671), RI (LAO00065), TX (T104704476), VT (VT-0935),
VA (460195), USDA (Permit #525-23-122-91930).
(508) 896-1706Phone:
The original project report/data package is held by Alpha Analytical. This report/data package is paginated and should be reproduced only in its
entirety. Alpha Analytical holds no responsibility for results and/or data that are not consistent with the original.
Serial_No:11132310:56
Page 1 of 21
L2365178-01
L2365178-02
L2365178-03
Alpha
Sample ID
INFLUENT
EFFLUENT
EFFLUENT
Client ID
BREWSTER, MA
BREWSTER, MA
BREWSTER, MA
Sample
Location
PLEASANT BAY
K47810DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178
11/13/23
11/02/23 13:45
11/02/23 13:45
11/02/23 13:45
Collection
Date/TimeMatrix Receive Date
WATER
WATER
WATER
11/02/23
11/02/23
11/02/23
Serial_No:11132310:56
Page 2 of 21
PLEASANT BAY
K47810DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178
11/13/23
Case Narrative
The samples were received in accordance with the Chain of Custody and no significant deviations were encountered during the preparation
or analysis unless otherwise noted. Sample Receipt, Container Information, and the Chain of Custody are located at the back of the report.
Results contained within this report relate only to the samples submitted under this Alpha Lab Number and meet NELAP requirements for all
NELAP accredited parameters unless otherwise noted in the following narrative. The data presented in this report is organized by parameter
(i.e. VOC, SVOC, etc.). Sample specific Quality Control data (i.e. Surrogate Spike Recovery) is reported at the end of the target analyte list
for each individual sample, followed by the Laboratory Batch Quality Control at the end of each parameter. Tentatively Identified
Compounds (TICs), if requested, are reported for compounds identified to be present and are not part of the method/program Target
Compound List, even if only a subset of the TCL are being reported. If a sample was re-analyzed or re-extracted due to a required quality
control corrective action and if both sets of data are reported, the Laboratory ID of the re-analysis or re-extraction is designated with an "R"
or "RE", respectively.
When multiple Batch Quality Control elements are reported (e.g. more than one LCS), the associated samples for each element are noted in
the grey shaded header line of each data table. Any Laboratory Batch, Sample Specific % recovery or RPD value that is outside the listed
Acceptance Criteria is bolded in the report. In reference to questions H (CAM) or 4 (RCP) when "NO" is checked, the performance criteria
for CAM and RCP methods allow for some quality control failures to occur and still be within method compliance. In these instances, the
specific failure is not narrated but noted in the associated QC Outlier Summary Report, located directly after the Case Narrative. QC
information is also incorporated in the Data Usability Assessment table (Format 11) of our Data Merger tool, where it can be reviewed in
conjunction with the sample result, associated regulatory criteria and any associated data usability implications.
Soil/sediments, solids and tissues are reported on a dry weight basis unless otherwise noted. Definitions of all data qualifiers and acronyms
used in this report are provided in the Glossary located at the back of the report.
HOLD POLICY - For samples submitted on hold, Alpha's policy is to hold samples (with the exception of Air canisters) free of charge for 21
calendar days from the date the project is completed. After 21 calendar days, we will dispose of all samples submitted including those put
on hold unless you have contacted your Alpha Project Manager and made arrangements for Alpha to continue to hold the samples. Air
canisters will be disposed after 3 business days from the date the project is completed.
Please contact Project Management at 800-624-9220 with any questions.
Serial_No:11132310:56
Page 3 of 21
Case Narrative (continued)
PLEASANT BAY
K47810DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178
11/13/23
Coliform, Fecal (MF)
L2365178-03: The sample has an elevated detection limit due to the dilution required by the method.
OIL & GREASE, HEM-GRAV
The WG1851194-4 MS recovery, performed on L2365178-02, is outside the acceptance criteria for oil &
grease, hem-grav (70%); however, the associated LCS recovery is within criteria. No further action was taken.
BOD, 5 day
The WG1848170-4 MS recovery, performed on L2365178-02, is outside the acceptance criteria for bod, 5 day
(392%); however, the associated LCS recovery is within criteria. No further action was taken.
I, the undersigned, attest under the pains and penalties of perjury that, to the best of my knowledge and
belief and based upon my personal inquiry of those responsible for providing the information contained
in this analytical report, such information is accurate and complete. This certificate of analysis is not
complete unless this page accompanies any and all pages of this report.
Authorized Signature:
Title: Technical Director/Representative Date: 11/13/23
Serial_No:11132310:56
Page 4 of 21
INORGANICS
&
MISCELLANEOUS
Serial_No:11132310:56
Page 5 of 21
FF
INFLUENTClient ID:
11/02/23 13:45Date Collected:
11/02/23Date Received:
Parameter Result
Dilution
Factor
Matrix:Water
BREWSTER, MASample Location:
L2365178-01Lab ID:
Qualifier Units RL
SAMPLE RESULTS
Project Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
Field Prep:
Date
Analyzed
Analytical
Method Analyst
Not Specified
General Chemistry - Westborough Lab
Solids, Total
Solids, Total Suspended
Nitrogen, Ammonia
BOD, 5 day
300
83.
16.2
130
mg/l
mg/l
mg/l
mg/l
1.3
4
5
15
13
20
0.375
30
11/06/23 05:15
11/03/23 19:16
11/10/23 11:54
11/08/23 12:40
121,2540B
121,2540D
121,4500NH3-BH
121,5210B
DEW
REM
KEP
OCF
Date
Prepared
-
-
11/06/23 22:26
11/03/23 10:00
11/13/23
MDL
NA
NA
--
NA
Sample Depth:
Serial_No:11132310:56
Page 6 of 21
FF
EFFLUENTClient ID:
11/02/23 13:45Date Collected:
11/02/23Date Received:
Parameter Result
Dilution
Factor
Matrix:Water
BREWSTER, MASample Location:
L2365178-02Lab ID:
Qualifier Units RL
SAMPLE RESULTS
Project Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
Field Prep:
Date
Analyzed
Analytical
Method Analyst
Not Specified
General Chemistry - Westborough Lab
Solids, Total
Solids, Total Suspended
Chloride
Nitrogen, Nitrite
Nitrogen, Nitrate
Nitrogen, Total Kjeldahl
BOD, 5 day
Oil & Grease, Hem-Grav
240
ND
48.
ND
0.90
0.715
ND
ND
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
1.3
1
1
1
1
1
1
.9
13
5.0
1.0
0.050
0.10
0.300
2.0
3.6
11/06/23 05:15
11/03/23 19:16
11/10/23 14:36
11/03/23 03:58
11/03/23 03:58
11/10/23 20:26
11/08/23 20:09
11/11/23 17:22
121,2540B
121,2540D
121,4500CL-E
44,353.2
44,353.2
121,4500NH3-H
121,5210B
140,1664B
DEW
REM
JER
KAF
KAF
AT
JRG
QJM
Date
Prepared
-
-
-
-
-
11/04/23 15:28
11/03/23 22:19
11/11/23 14:30
11/13/23
MDL
NA
NA
--
--
--
--
NA
--
Sample Depth:
Serial_No:11132310:56
Page 7 of 21
FF
EFFLUENTClient ID:
11/02/23 13:45Date Collected:
11/02/23Date Received:
Parameter Result
Dilution
Factor
Matrix:Water
BREWSTER, MASample Location:
L2365178-03Lab ID:
Qualifier Units RL
SAMPLE RESULTS
Project Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
Field Prep:
Date
Analyzed
Analytical
Method Analyst
Not Specified
Microbiological Analysis - Westborough Lab
Coliform, Fecal (MF)ND col/100ml 22.0 11/02/23 19:07 121,9222D JAI
Date
Prepared
-
11/13/23
MDL
NA
Sample Depth:
Serial_No:11132310:56
Page 8 of 21
FF
Parameter Result
Dilution
FactorQualifierUnitsRL
Method Blank Analysis
Batch Quality Control
Project Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
Date
Analyzed
Analytical
Method Analyst
Date
Prepared
11/13/23
Coliform, Fecal (MF)
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Solids, Total Suspended
BOD, 5 day
Nitrogen, Total Kjeldahl
Solids, Total
Nitrogen, Ammonia
Chloride
Oil & Grease, Hem-Grav
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
col/100ml
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
1
1
1
1
1
1
1
1
1
1
1
1.0
0.050
0.10
2.0
5.0
2.0
0.300
10
0.075
1.0
4.0
11/02/23 19:07
11/03/23 02:59
11/03/23 03:06
11/08/23 12:40
11/03/23 19:16
11/08/23 20:09
11/10/23 20:21
11/06/23 05:15
11/10/23 11:26
11/10/23 13:37
11/11/23 16:33
121,9222D
44,353.2
44,353.2
121,5210B
121,2540D
121,5210B
121,4500NH3-H
121,2540B
121,4500NH3-BH
121,4500CL-E
140,1664B
JAI
KAF
KAF
OCF
REM
JRG
AT
DEW
KEP
JER
QJM
-
-
-
11/03/23 10:00
-
11/03/23 22:19
11/04/23 15:28
-
11/06/23 22:26
-
11/11/23 14:30
Microbiological Analysis - Westborough Lab for sample(s): 03 Batch: WG1847700-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1847764-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1847770-1
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1847819-1
General Chemistry - Westborough Lab for sample(s): 01-02 Batch: WG1848168-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1848170-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1848317-1
General Chemistry - Westborough Lab for sample(s): 01-02 Batch: WG1848591-1
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1848844-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1850842-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1851194-1
MDL
NA
--
--
NA
NA
NA
--
NA
--
--
--
Serial_No:11132310:56
Page 9 of 21
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Solids, Total Suspended
BOD, 5 day
Nitrogen, Total Kjeldahl
Solids, Total
102
104
100
97
103
93
90
-
-
-
-
-
-
-
90-110
90-110
85-115
80-120
85-115
78-122
80-120
-
-
-
-
-
-
-
20
20
20
Parameter
LCS
%Recovery
LCSD
%Recovery
%Recovery
Limits RPD RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1847764-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1847770-2
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1847819-2
General Chemistry - Westborough Lab Associated sample(s): 01-02 Batch: WG1848168-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1848170-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1848317-2
General Chemistry - Westborough Lab Associated sample(s): 01-02 Batch: WG1848591-2
Lab Control Sample Analysis
Batch Quality ControlProject Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
11/13/23
Qual Qual Qual
Serial_No:11132310:56
Page 10 of 21
Nitrogen, Ammonia
Chloride
Oil & Grease, Hem-Grav
101
103
100
-
-
-
80-120
90-110
78-114
-
-
-
20
18
Parameter
LCS
%Recovery
LCSD
%Recovery
%Recovery
Limits RPD RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1848844-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1850842-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1851194-2
Lab Control Sample Analysis
Batch Quality ControlProject Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
11/13/23
Serial_No:11132310:56
Page 11 of 21
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
BOD, 5 day
Nitrogen, Total Kjeldahl
Nitrogen, Ammonia
Chloride
Oil & Grease, Hem-Grav
0.15
5.3
130
ND
ND
ND
28
ND
4.9
10
310
390
6.78
4.07
51
26
119
118
87
392
85
102
115
70
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
80-120
83-113
50-145
50-145
77-111
80-120
58-140
78-114
-
-
-
-
-
-
-
-
20
6
35
35
24
20
7
18
Parameter
Native
Sample
MS
Found
MS
%Recovery
MSD
Found
MSD
%Recovery
Recovery
Limits RPD
RPD
Limits
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1847764-4 QC Sample: L2364994-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1847770-4 QC Sample: L2364994-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1847819-4 QC Sample: L2365178-01 Client ID: INFLUENT
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1848170-4 QC Sample: L2365178-02 Client ID: EFFLUENT
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1848317-4 QC Sample: L2349794-56 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1848844-4 QC Sample: L2365134-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1850842-4 QC Sample: L2365024-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1851194-4 QC Sample: L2365178-02 Client ID: EFFLUENT
4
4
200
100
8
4
20
37.7
MS
Added
Matrix Spike Analysis
Batch Quality Control
Project Name:
Project Number:
Lab Number:
Report Date:
PLEASANT BAY
K47810DA.S.WW.700
L2365178
11/13/23
Qual
Q
Q
Q
Qual Qual
Serial_No:11132310:56
Page 12 of 21
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Solids, Total Suspended
Solids, Total Suspended
BOD, 5 day
Nitrogen, Total Kjeldahl
Solids, Total
Nitrogen, Ammonia
0.15
5.3
130
56
310
ND
ND
510
ND
0.14
5.4
140
57
320
ND
ND
520
0.097
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
7
2
2
2
3
NC
NC
2
NC
20
6
35
32
32
35
24
16
20
Units RPDParameterNative Sample Duplicate Sample RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1847764-3 QC Sample: L2364994-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1847770-3 QC Sample: L2364994-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1847819-3 QC Sample: L2365178-01 Client ID: INFLUENT
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1848168-3 QC Sample: L2365096-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1848168-4 QC Sample: L2365157-02 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1848170-3 QC Sample: L2365178-02 Client ID: EFFLUENT
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1848317-3 QC Sample: L2349794-56 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1848591-3 QC Sample: L2364610-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1848844-3 QC Sample: L2365134-01 Client ID: DUP Sample
PLEASANT BAY
K47810DA.S.WW.700
Project Name:
Project Number:
L2365178Lab Number:
Report Date:
Lab Duplicate Analysis
Batch Quality Control
11/13/23
Qual
Serial_No:11132310:56
Page 13 of 21
Chloride
Oil & Grease, Hem-Grav
28
ND
31
ND
mg/l
mg/l
10
NC
7
18
Units RPDParameterNative Sample Duplicate Sample RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1850842-3 QC Sample: L2365024-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1851194-3 QC Sample: L2365081-02 Client ID: DUP Sample
PLEASANT BAY
K47810DA.S.WW.700
Project Name:
Project Number:
L2365178Lab Number:
Report Date:
Lab Duplicate Analysis
Batch Quality Control
11/13/23
Q
Serial_No:11132310:56
Page 14 of 21
*Values in parentheses indicate holding time in days
L2365178-01A
L2365178-01B
L2365178-01C
L2365178-02A
L2365178-02B
L2365178-02C
L2365178-02D
L2365178-02E
L2365178-03A
L2365178-03B
Plastic 500ml H2SO4 preserved
Plastic 950ml unpreserved
Plastic 950ml unpreserved
Plastic 250ml H2SO4 preserved
Plastic 950ml unpreserved
Plastic 950ml unpreserved
Amber 1000ml HCl preserved
Amber 1000ml HCl preserved
Bacteria Cup Na2S2O3 preserved
Bacteria Cup Na2S2O3 preserved
A
A
A
A
A
A
A
A
A
A
<2
7
7
<2
7
7
NA
NA
NA
NA
3.4
3.4
3.4
3.4
3.4
3.4
3.4
3.4
3.4
3.4
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Absent
Absent
Absent
Absent
Absent
Absent
Absent
Absent
Absent
Absent
A Absent
Cooler Custody Seal
Cooler Information
PLEASANT BAY
K47810DA.S.WW.700
NH3-4500(28)
TSC-2540(7),BOD-5210(2)
TSS-2540(7)
TKN-4500(28)
TSC-2540(7),CL-4500(28),NO2-353(2),NO3-
353(2),BOD-5210(2)
TSS-2540(7)
OG-1664(28)
OG-1664(28)
F-COLI-MF(.33)
F-COLI-MF(.33)
Project Name:
Project Number:
L2365178Lab Number:
Report Date:
Sample Receipt and Container Information
Container ID Container Type Cooler
Temp
deg C Pres Seal
Container Information
Analysis(*)
11/13/23
Were project specific reporting limits specified?YES
<2
7
7
<2
7
7
Frozen
Date/Time
Final
pH
Initial
pH
Serial_No:11132310:56
Page 15 of 21
Report Format:Data Usability Report
GLOSSARY
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178PLEASANT BAY
K47810DA.S.WW.700 11/13/23
Acronyms
DL
EDL
EMPC
EPA
LCS
LCSD
LFB
LOD
LOQ
MDL
MS
MSD
NA
NC
NDPA/DPA
NI
NP
NR
RL
RPD
SRM
STLP
TEF
TEQ
TIC
Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated values, when
those target analyte concentrations are quantified below the limit of quantitation (LOQ). The DL includes any adjustments
from dilutions, concentrations or moisture content, where applicable. (DoD report formats only.)
Estimated Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated
values, when those target analyte concentrations are quantified below the reporting limit (RL). The EDL includes any
adjustments from dilutions, concentrations or moisture content, where applicable. The use of EDLs is specific to the analysis
of PAHs using Solid-Phase Microextraction (SPME).
Estimated Maximum Possible Concentration: The concentration that results from the signal present at the retention time of an
analyte when the ions meet all of the identification criteria except the ion abundance ratio criteria. An EMPC is a worst-case
estimate of the concentration.
Environmental Protection Agency.
Laboratory Control Sample: A sample matrix, free from the analytes of interest, spiked with verified known amounts of
analytes or a material containing known and verified amounts of analytes.
Laboratory Control Sample Duplicate: Refer to LCS.
Laboratory Fortified Blank: A sample matrix, free from the analytes of interest, spiked with verified known amounts of
analytes or a material containing known and verified amounts of analytes.
Limit of Detection: This value represents the level to which a target analyte can reliably be detected for a specific analyte in a
specific matrix by a specific method. The LOD includes any adjustments from dilutions, concentrations or moisture content,
where applicable. (DoD report formats only.)
Limit of Quantitation: The value at which an instrument can accurately measure an analyte at a specific concentration. The
LOQ includes any adjustments from dilutions, concentrations or moisture content, where applicable. (DoD report formats
only.)
Limit of Quantitation: The value at which an instrument can accurately measure an analyte at a specific concentration. The
LOQ includes any adjustments from dilutions, concentrations or moisture content, where applicable. (DoD report formats
only.)
Method Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated
values, when those target analyte concentrations are quantified below the reporting limit (RL). The MDL includes any
adjustments from dilutions, concentrations or moisture content, where applicable.
Matrix Spike Sample: A sample prepared by adding a known mass of target analyte to a specified amount of matrix sample for
which an independent estimate of target analyte concentration is available. For Method 332.0, the spike recovery is calculated
using the native concentration, including estimated values.
Matrix Spike Sample Duplicate: Refer to MS.
Not Applicable.
Not Calculated: Term is utilized when one or more of the results utilized in the calculation are non-detect at the parameter's
reporting unit.
N-Nitrosodiphenylamine/Diphenylamine.
Not Ignitable.
Non-Plastic: Term is utilized for the analysis of Atterberg Limits in soil.
No Results: Term is utilized when 'No Target Compounds Requested' is reported for the analysis of Volatile or Semivolatile
Organic TIC only requests.
Reporting Limit: The value at which an instrument can accurately measure an analyte at a specific concentration. The RL
includes any adjustments from dilutions, concentrations or moisture content, where applicable.
Relative Percent Difference: The results from matrix and/or matrix spike duplicates are primarily designed to assess the
precision of analytical results in a given matrix and are expressed as relative percent difference (RPD). Values which are less
than five times the reporting limit for any individual parameter are evaluated by utilizing the absolute difference between the
values; although the RPD value will be provided in the report.
Standard Reference Material: A reference sample of a known or certified value that is of the same or similar matrix as the
associated field samples.
Semi-dynamic Tank Leaching Procedure per EPA Method 1315.
Toxic Equivalency Factors: The values assigned to each dioxin and furan to evaluate their toxicity relative to 2,3,7,8-TCDD.
Toxic Equivalent: The measure of a sample's toxicity derived by multiplying each dioxin and furan by its corresponding TEF
and then summing the resulting values.
Tentatively Identified Compound: A compound that has been identified to be present and is not part of the target compound
list (TCL) for the method and/or program. All TICs are qualitatively identified and reported as estimated concentrations.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Serial_No:11132310:56
Page 16 of 21
Report Format:Data Usability Report
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178PLEASANT BAY
K47810DA.S.WW.700 11/13/23
Terms
Analytical Method: Both the document from which the method originates and the analytical reference method. (Example: EPA 8260B is
shown as 1,8260B.) The codes for the reference method documents are provided in the References section of the Addendum.
Chlordane: The target compound Chlordane (CAS No. 57-74-9) is reported for GC ECD analyses. Per EPA,this compound "refers to a
mixture of chlordane isomers, other chlorinated hydrocarbons and numerous other components." (Reference: USEPA Toxicological Review
of Chlordane, In Support of Summary Information on the Integrated Risk Information System (IRIS), December 1997.)
Difference: With respect to Total Oxidizable Precursor (TOP) Assay analysis, the difference is defined as the Post-Treatment value minus the
Pre-Treatment value.
Final pH: As it pertains to Sample Receipt & Container Information section of the report, Final pH reflects pH of container determined after
adjustment at the laboratory, if applicable. If no adjustment required, value reflects Initial pH.
Frozen Date/Time: With respect to Volatile Organics in soil, Frozen Date/Time reflects the date/time at which associated Reagent Water-
preserved vials were initially frozen. Note: If frozen date/time is beyond 48 hours from sample collection, value will be reflected in 'bold'.
Gasoline Range Organics (GRO): Gasoline Range Organics (GRO) results include all chromatographic peaks eluting from Methyl tert butyl
ether through Naphthalene, with the exception of GRO analysis in support of State of Ohio programs, which includes all chromatographic
peaks eluting from Hexane through Dodecane.
Initial pH: As it pertains to Sample Receipt & Container Information section of the report, Initial pH reflects pH of container determined upon
receipt, if applicable.
PAH Total: With respect to Alkylated PAH analyses, the 'PAHs, Total' result is defined as the summation of results for all or a subset of the
following compounds: Naphthalene, C1-C4 Naphthalenes, 2-Methylnaphthalene, 1-Methylnaphthalene, Biphenyl, Acenaphthylene,
Acenaphthene, Fluorene, C1-C3 Fluorenes, Phenanthrene, C1-C4 Phenanthrenes/Anthracenes, Anthracene, Fluoranthene, Pyrene, C1-C4
Fluoranthenes/Pyrenes, Benz(a)anthracene, Chrysene, C1-C4 Chrysenes, Benzo(b)fluoranthene, Benzo(j)+(k)fluoranthene, Benzo(e)pyrene,
Benzo(a)pyrene, Perylene, Indeno(1,2,3-cd)pyrene, Dibenz(ah)+(ac)anthracene, Benzo(g,h,i)perylene. If a 'Total' result is requested, the
results of its individual components will also be reported.
PFAS Total: With respect to PFAS analyses, the 'PFAS, Total (5)' result is defined as the summation of results for: PFHpA, PFHxS, PFOA,
PFNA and PFOS. In addition, the 'PFAS, Total (6)' result is defined as the summation of results for: PFHpA, PFHxS, PFOA, PFNA, PFDA
and PFOS. For MassDEP DW compliance analysis only, the 'PFAS, Total (6)' result is defined as the summation of results at or above the
RL. Note: If a 'Total' result is requested, the results of its individual components will also be reported.
Total: With respect to Organic analyses, a 'Total' result is defined as the summation of results for individual isomers or Aroclors. If a 'Total'
result is requested, the results of its individual components will also be reported. This is applicable to 'Total' results for methods 8260, 8081
and 8082.
Data Qualifiers
A
B
C
D
E
F
G
H
I
J
M
-
-
-
-
-
-
-
-
-
-
-
Spectra identified as "Aldol Condensates" are byproducts of the extraction/concentration procedures when acetone is introduced in
the process.
The analyte was detected above the reporting limit in the associated method blank. Flag only applies to associated field samples that
have detectable concentrations of the analyte at less than ten times (10x) the concentration found in the blank. For MCP-related
projects, flag only applies to associated field samples that have detectable concentrations of the analyte at less than ten times (10x)
the concentration found in the blank. For DOD-related projects, flag only applies to associated field samples that have detectable
concentrations of the analyte at less than ten times (10x) the concentration found in the blank AND the analyte was detected above
one-half the reporting limit (or above the reporting limit for common lab contaminants) in the associated method blank. For NJ-
Air-related projects, flag only applies to associated field samples that have detectable concentrations of the analyte above the
reporting limit. For NJ-related projects (excluding Air), flag only applies to associated field samples that have detectable
concentrations of the analyte, which was detected above the reporting limit in the associated method blank or above five times the
reporting limit for common lab contaminants (Phthalates, Acetone, Methylene Chloride, 2-Butanone).
Co-elution: The target analyte co-elutes with a known lab standard (i.e. surrogate, internal standards, etc.) for co-extracted
analyses.
Concentration of analyte was quantified from diluted analysis. Flag only applies to field samples that have detectable concentrations
of the analyte.
Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
The ratio of quantifier ion response to qualifier ion response falls outside of the laboratory criteria. Results are considered to be an
estimated maximum concentration.
The concentration may be biased high due to matrix interferences (i.e, co-elution) with non-target compound(s). The result should
be considered estimated.
The analysis of pH was performed beyond the regulatory-required holding time of 15 minutes from the time of sample collection.
The lower value for the two columns has been reported due to obvious interference.
Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
Reporting Limit (RL) exceeds the MCP CAM Reporting Limit for this analyte.
1 The reference for this analyte should be considered modified since this analyte is absent from the target analyte list of the
original method.
-
Footnotes
Serial_No:11132310:56
Page 17 of 21
Report Format:Data Usability Report
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178PLEASANT BAY
K47810DA.S.WW.700 11/13/23
Data Qualifiers
ND
NJ
P
Q
R
RE
S
V
Z
-
-
-
-
-
-
-
-
-
Not detected at the reporting limit (RL) for the sample.
Presumptive evidence of compound. This represents an estimated concentration for Tentatively Identified Compounds (TICs), where
the identification is based on a mass spectral library search.
The RPD between the results for the two columns exceeds the method-specified criteria.
The quality control sample exceeds the associated acceptance criteria. For DOD-related projects, LCS and/or Continuing Calibration
Standard exceedences are also qualified on all associated sample results. Note: This flag is not applicable for matrix spike recoveries
when the sample concentration is greater than 4x the spike added or for batch duplicate RPD when the sample concentrations are less
than 5x the RL. (Metals only.)
Analytical results are from sample re-analysis.
Analytical results are from sample re-extraction.
Analytical results are from modified screening analysis.
The surrogate associated with this target analyte has a recovery outside the QC acceptance limits. (Applicable to MassDEP DW
Compliance samples only.)
The batch matrix spike and/or duplicate associated with this target analyte has a recovery/RPD outside the QC acceptance limits.
(Applicable to MassDEP DW Compliance samples only.)
Serial_No:11132310:56
Page 18 of 21
Alpha Analytical performs services with reasonable care and diligence normal to the analytical testing
laboratory industry. In the event of an error, the sole and exclusive responsibility of Alpha Analytical
shall be to re-perform the work at it's own expense. In no event shall Alpha Analytical be held liable
for any incidental, consequential or special damages, including but not limited to, damages in any way
connected with the use of, interpretation of, information or analysis provided by Alpha Analytical.
We strongly urge our clients to comply with EPA protocol regarding sample volume, preservation, cooling,
containers, sampling procedures, holding time and splitting of samples in the field.
LIMITATION OF LIABILITIES
44
121
140
Methods for the Determination of Inorganic Substances in Environmental Samples,
EPA/600/R-93/100, August 1993.
Standard Methods for the Examination of Water and Wastewater. APHA-AWWA-WEF.
Standard Methods Online.
Method 1664,Revision B: N-Hexane Extractable Material (HEM; Oil & Grease) and
Silica Gel Treated N-Hexane Extractable Material (SGT-HEM; Non-polar Material) by
Extraction and Gravimetry, EPA-821-R-10-001, February 2010.
Project Name:
Project Number:
Lab Number:
Report Date:
L2365178PLEASANT BAY
K47810DA.S.WW.700
REFERENCES
11/13/23
Serial_No:11132310:56
Page 19 of 21
Alpha Analytical, Inc.ID No.:17873
Facility: Company-wide Revision 20
Department: Quality Assurance Published Date: 6/16/2023 4:52:28 PM
Title: Certificate/Approval Program Summary Page 1 of 1
Document Type: Form Pre-Qualtrax Document ID: 08-113
Certification Information
The following analytes are not included in our Primary NELAP Scope of Accreditation:
Westborough Facility
EPA 624.1: m/p-xylene, o-xylene, Naphthalene
EPA 625.1: alpha-Terpineol
EPA 8260D: NPW: 1,2,4,5-Tetramethylbenzene; 4-Ethyltoluene, Azobenzene; SCM: Iodomethane (methyl iodide), 1,2,4,5-Tetramethylbenzene; 4-
Ethyltoluene.
EPA 8270E: NPW: Dimethylnaphthalene,1,4-Diphenylhydrazine, alpha-Terpineol; SCM: Dimethylnaphthalene,1,4-Diphenylhydrazine.
SM4500: NPW: Amenable Cyanide; SCM: Total Phosphorus, TKN, NO2, NO3.
Mansfield Facility
SM 2540D: TSS.
EPA TO-15: Halothane, 2,4,4-Trimethyl-2-pentene, 2,4,4-Trimethyl-1-pentene, Thiophene, 2-Methylthiophene,
3-Methylthiophene, 2-Ethylthiophene, 1,2,3-Trimethylbenzene, Indan, Indene, 1,2,4,5-Tetramethylbenzene, Benzothiophene, 1-Methylnaphthalene.
Biological Tissue Matrix: EPA 3050B
The following analytes are included in our Massachusetts DEP Scope of Accreditation
Westborough Facility:
Drinking Water
EPA 300.0: Chloride, Nitrate-N, Fluoride, Sulfate; EPA 353.2: Nitrate-N, Nitrite-N; SM4500NO3-F: Nitrate-N, Nitrite-N; SM4500F-C, SM4500CN-CE,
EPA 180.1, SM2130B, SM4500Cl-D, SM2320B, SM2540C, SM4500H-B, SM4500NO2-B
EPA 524.2: THMs and VOCs; EPA 504.1: EDB, DBCP.
Microbiology: SM9215B; SM9223-P/A, SM9223B-Colilert-QT,SM9222D.
Non-Potable Water
SM4500H,B, EPA 120.1, SM2510B, SM2540C, SM2320B, SM4500CL-E, SM4500F-BC, SM4500NH3-BH: Ammonia-N and Kjeldahl-N, EPA 350.1:
Ammonia-N, LACHAT 10-107-06-1-B: Ammonia-N, EPA 351.1, SM4500NO3-F, EPA 353.2: Nitrate-N, SM4500P-E, SM4500P-B, E, SM4500SO4-E,
SM5220D, EPA 410.4, SM5210B, SM5310C, SM4500CL-D, EPA 1664, EPA 420.1, SM4500-CN-CE, SM2540D, EPA 300: Chloride, Sulfate, Nitrate.
EPA 624.1: Volatile Halocarbons & Aromatics,
EPA 608.3: Chlordane, Toxaphene, Aldrin, alpha-BHC, beta-BHC, gamma-BHC, delta-BHC, Dieldrin, DDD, DDE, DDT, Endosulfan I, Endosulfan II,
Endosulfan sulfate, Endrin, Endrin Aldehyde, Heptachlor, Heptachlor Epoxide, PCBs
EPA 625.1: SVOC (Acid/Base/Neutral Extractables).
Microbiology: SM9223B-Colilert-QT; Enterolert-QT, SM9221E, EPA 1600, EPA 1603, SM9222D.
Mansfield Facility:
Drinking Water
EPA 200.7: Al, Ba, Cd, Cr, Cu, Fe, Mn, Ni, Na, Ag, Ca, Zn. EPA 200.8: Al, Sb, As, Ba, Be, Cd, Cr, Cu, Pb, Mn, Ni, Se, Ag, TL, Zn. EPA 245.1 Hg.
EPA 522, EPA 537.1.
Non-Potable Water
EPA 200.7: Al, Sb, As, Be, Cd, Ca, Cr, Co, Cu, Fe, Pb, Mg, Mn, Mo, Ni, K, Se, Ag, Na, Sr, TL, Ti, V, Zn.
EPA 200.8: Al, Sb, As, Be, Cd, Cr, Cu, Fe, Pb, Mn, Ni, K, Se, Ag, Na, TL, Zn.
EPA 245.1 Hg.
SM2340B
For a complete listing of analytes and methods, please contact your Alpha Project Manager.
Serial_No:11132310:56
Page 20 of 21
Serial_No:11132310:56
Page 21 of 21
Massachusetts Department of Environmental Protection
eDEP Transaction Copy
Here is the file you requested for your records.
To retain a copy of this file you must save and/or print.
Username:
Transaction ID:
Document:
Size of File:
Status of Transaction:
Date and Time Created:
Note: This file only includes forms that were part of your
transaction as of the date and time indicated above. If you need
a more current copy of your transaction, return to eDEP and
select to “Download a Copy” from the Current Submittals page.
1650445
12/14/2023:2:39:11 PM
1083.91K
SFARRENKOPF
Groundwater Discharge Monitoring Report Forms
In Process
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
MAPLEWOOD AT BREWSTER
a. Name
820 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
JOSEPH SMITH
a. Name of Facility Contact Person
7742125005 jsmith@nsuwater.com
b. Telephone Number c. email address
3. Sampling information:
11/1/2023 NOT APPLICABLE
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
BEA/NSU WWTO PERSONNEL
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Daily Log Sheet 2023 Nov Daily
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DAILY LOG SHEET
951
1. Permit Number
465405799
2. Tax identification Number
2023 NOV DAILY
3. Sampling Month & Frequency
C. Daily Readings/Analysis Information
Date Effluent
Flow GPD
Reuse
Flow GPD
Irrigation
Flow GPD
Turbidity Influent pH Effluent
pH
Chlorine
Residual
(mg/l)
UV
Intensity
(%)
1 12398 6.9 7.2
2 4381 7.0 7.2
3 5269 6.9 6.8
4 5269
5 5269
6 5202 6.8 6.8
7 7157 6.8
8 6591 6.9 7.0
9 5279 6.7 7.0
10 6294 7.6
11 6294
12 6294
13 7456 6.9 7.4
14 6185 6.8 7.1
15 4921 6.9 6.9
16 6471 6.9 7.0
17 7195 6.8
18 7195
19 7195
20 13918 6.8 6.9
21 9720 6.8 6.8
22 6239 6.9
23 6239
24 6239
25 6239
26 6239
27 14189 6.9 7.1
28 10816 6.8 6.8
29 7995 6.9 7.0
30 8945 6.8 7.3
31
gdpdls.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DAILY LOG SHEET
951
1. Permit Number
465405799
2. Tax identification Number
2023 NOV DAILY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
MAPLEWOOD AT BREWSTER
a. Name
820 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
JOSEPH SMITH
a. Name of Facility Contact Person
7742125005 jsmith@nsuwater.com
b. Telephone Number c. email address
3. Sampling information:
11/16/2023 ALPHA ANALYTICAL
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
ALPHA ANALYTICAL PERSONNEL
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Discharge Monitoring Report 2023 Nov Monthly
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DISCHARGE MONITORING REPORT
951
1. Permit Number
465405799
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
D. Contaminant Analysis Information
For "0", below detection limit, less than (<) value, or not detected, enter "ND"
TNTC = too numerous to count. (Fecal results only)
NS = Not Sampled
1. Parameter/Contaminant 2. Influent 3. Effluent 4. Effluent Method
Units Detection limit
BOD 77 ND 2.0
MG/L
TSS 32 ND 5.0
MG/L
TOTAL SOLIDS 380
MG/L
AMMONIAN 14.6
MG/L
NITRATEN 12 0.50
MG/L
TOTAL NITROGEN(NO3+NO2+TKN)14.42 1.15
MG/L
OIL & GREASE ND 3.6
MG/L
infeffrpblank.doc • rev. 09/15/15 Groundwater Permit Discharge Monitoring Report • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DISCHARGE MONITORING REPORT
951
1. Permit Number
465405799
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
MAPLEWOOD AT BREWSTER
a. Name
820 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
JOSEPH SMITH
a. Name of Facility Contact Person
7742125005 jsmith@nsuwater.com
b. Telephone Number c. email address
3. Sampling information:
11/16/2023 ALPHA ANALYTICAL
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
ALPHA ANALYTICAL PERSONNEL
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Monitoring Well Data Report 2023 Nov Monthly
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
MONITORING WELL DATA REPORT
951
1. Permit Number
465405799
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
C. Contaminant Analysis Information
For "0", below detection limit, less than (<) value, or not detected, enter "ND"
TNTC = too numerous to count. (Fecal results only)
NS = Not Sampled
DRY = Not enough water in well to sample.
<
Parameter/Contaminant MW1 MW2 MW3 MW4
Units Well #: 1 Well #: 2 Well #: 3 Well #: 4 Well #: 5 Well #: 6
PH 6.84 6.52 6.67 6.91
S.U.
STATIC WATER LEVEL 33.25 32.13 32.68 32.31
FEET
SPECIFIC CONDUCTANCE 168.1 193.4 202.6 165.0
UMHOS/C
mwdgwpblank.doc • rev. 09/15/15 Monitoring Well Data for Groundwater Permit • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
MONITORING WELL DATA REPORT
951
1. Permit Number
465405799
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
Any person signing
a document under
314 CMR 5.14(1) or
(2) shall make the
following
certification
If you are filing
electronically and
want to attach
additional
comments, select
the check box.
Facility Information
MAPLEWOOD AT BREWSTER
a. Name
820 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
Certification
“I certify under penalty of law that this document and all attachments were prepared under my direction or supervision in
accordance with a system designed to assure that qualified personnel properly gather and evaluate the information submitted.
Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate and complete. I am aware that there
are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations.”
SAMANTHA FARRENKOPF 12/14/2023
a. Signature b. Date (mm/dd/yyyy)
Reporting Package Comments
BENNETT ENVIRONMENTAL ASSOCIATES, LLC. (BEA) HAS COMPLETED THE NOVEMBER
2023 MONTHLY INFLUENT AND EFFLUENT SAMPLING OF THE BIOCLERE WASTEWATER
TREATMENT SYSTEM. MONTHLY WASTEWATER SAMPLING WAS COMPLETED ON 11/16/23.
LABORATORY RESULTS REPORTED NITRATE AND TOTAL NITROGEN GREATER THAN
DISCHARGE PERMIT LIMITS. EFFLUENT RESAMPLING COMPLETED ON 12/5/23 FOR
ANALYSIS OF NITRATE AND TOTAL NITROGEN REPORTED CONCENTRATIONS OF 0.22 MG/L
AND 2.37 MG/L, RESPECTIVELY. EFFLUENT PH WAS REPORTED WITHIN THE 6.58.5 RANGE
THROUGHOUT THE MONTH. FLOW VOLUME MEASUREMENTS WERE ASSESSED DURING
THE MONTH FROM THE SYSTEM’S EFFLUENT FLOW METER. DAILY FLOW REMAINED
WITHIN THE 19,800GPD LIMITATION THROUGHOUT THE MONTH. THE MINIMUM, MAXIMUM
AND AVERAGE GPD FLOWS REPORTED OVER THE COURSE OF THE MONTH WERE 4,381
GPD, 14,189 GPD AND 7,303 GPD, RESPECTIVELY.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
951
1. Permit Number
465405799
2. Tax identification Number
L2368339
Bennett Environmental Associates
K10842DA.S.WW.700
MAPLEWOOD AT BREWSTER
Client:
Project Name:
Project Number:
11/27/23
Eight Walkup Drive, Westborough, MA 01581-1019
Lab Number:
Report Date:
508-898-9220 (Fax) 508-898-9193 800-624-9220 - www.alphalab.com
1573 Main Street
Brewster, MA 02631
Samantha FarrenkopfATTN:
ANALYTICAL REPORT
Certifications & Approvals: MA (M-MA086), NH NELAP (2064), CT (PH-0826), IL (200077), IN (C-MA-03), KY (KY98045), ME (MA00086), MD
(348), NJ (MA935), NY (11148), NC (25700/666), OH (CL108), OR (MA-1316), PA (68-03671), RI (LAO00065), TX (T104704476), VT (VT-0935),
VA (460195), USDA (Permit #525-23-122-91930).
(508) 896-1706Phone:
The original project report/data package is held by Alpha Analytical. This report/data package is paginated and should be reproduced only in its
entirety. Alpha Analytical holds no responsibility for results and/or data that are not consistent with the original.
Serial_No:11272318:05
Page 1 of 19
L2368339-01
L2368339-02
Alpha
Sample ID
INFLUENT
EFFLUENT
Client ID
BREWSTER, MA
BREWSTER, MA
Sample
Location
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339
11/27/23
11/16/23 11:00
11/16/23 11:30
Collection
Date/TimeMatrix Receive Date
WATER
WATER
11/16/23
11/16/23
Serial_No:11272318:05
Page 2 of 19
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339
11/27/23
Case Narrative
The samples were received in accordance with the Chain of Custody and no significant deviations were encountered during the preparation
or analysis unless otherwise noted. Sample Receipt, Container Information, and the Chain of Custody are located at the back of the report.
Results contained within this report relate only to the samples submitted under this Alpha Lab Number and meet NELAP requirements for all
NELAP accredited parameters unless otherwise noted in the following narrative. The data presented in this report is organized by parameter
(i.e. VOC, SVOC, etc.). Sample specific Quality Control data (i.e. Surrogate Spike Recovery) is reported at the end of the target analyte list
for each individual sample, followed by the Laboratory Batch Quality Control at the end of each parameter. Tentatively Identified
Compounds (TICs), if requested, are reported for compounds identified to be present and are not part of the method/program Target
Compound List, even if only a subset of the TCL are being reported. If a sample was re-analyzed or re-extracted due to a required quality
control corrective action and if both sets of data are reported, the Laboratory ID of the re-analysis or re-extraction is designated with an "R"
or "RE", respectively.
When multiple Batch Quality Control elements are reported (e.g. more than one LCS), the associated samples for each element are noted in
the grey shaded header line of each data table. Any Laboratory Batch, Sample Specific % recovery or RPD value that is outside the listed
Acceptance Criteria is bolded in the report. In reference to questions H (CAM) or 4 (RCP) when "NO" is checked, the performance criteria
for CAM and RCP methods allow for some quality control failures to occur and still be within method compliance. In these instances, the
specific failure is not narrated but noted in the associated QC Outlier Summary Report, located directly after the Case Narrative. QC
information is also incorporated in the Data Usability Assessment table (Format 11) of our Data Merger tool, where it can be reviewed in
conjunction with the sample result, associated regulatory criteria and any associated data usability implications.
Soil/sediments, solids and tissues are reported on a dry weight basis unless otherwise noted. Definitions of all data qualifiers and acronyms
used in this report are provided in the Glossary located at the back of the report.
HOLD POLICY - For samples submitted on hold, Alpha's policy is to hold samples (with the exception of Air canisters) free of charge for 21
calendar days from the date the project is completed. After 21 calendar days, we will dispose of all samples submitted including those put
on hold unless you have contacted your Alpha Project Manager and made arrangements for Alpha to continue to hold the samples. Air
canisters will be disposed after 3 business days from the date the project is completed.
Please contact Project Management at 800-624-9220 with any questions.
Serial_No:11272318:05
Page 3 of 19
Case Narrative (continued)
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339
11/27/23
Solids, Total Suspended
The WG1855029-2 LCS recovery for solids, total suspended (76%), associated with L2368339-02, is outside
the acceptance criteria. Due to the lack of additional sample, no further action was taken.
WG1855029: A Laboratory Duplicate was prepared with the sample batch, however, the native sample required
re-analysis; therefore, the result could not be reported.
I, the undersigned, attest under the pains and penalties of perjury that, to the best of my knowledge and
belief and based upon my personal inquiry of those responsible for providing the information contained
in this analytical report, such information is accurate and complete. This certificate of analysis is not
complete unless this page accompanies any and all pages of this report.
Authorized Signature:
Title: Technical Director/Representative Date: 11/27/23
Serial_No:11272318:05
Page 4 of 19
INORGANICS
&
MISCELLANEOUS
Serial_No:11272318:05
Page 5 of 19
FF
INFLUENTClient ID:
11/16/23 11:00Date Collected:
11/16/23Date Received:
Parameter Result
Dilution
Factor
Matrix:Water
BREWSTER, MASample Location:
L2368339-01Lab ID:
Qualifier Units RL
SAMPLE RESULTS
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2368339
Field Prep:
Date
Analyzed
Analytical
Method Analyst
Not Specified
General Chemistry - Westborough Lab
Solids, Total
Solids, Total Suspended
Nitrogen, Ammonia
BOD, 5 day
380
32.
14.6
77
mg/l
mg/l
mg/l
mg/l
1.3
2
5
15
13
10
0.375
30
11/21/23 05:06
11/22/23 20:56
11/21/23 21:50
11/22/23 12:00
121,2540B
121,2540D
121,4500NH3-BH
121,5210B
DEW
REM
AT
MKT
Date
Prepared
-
-
11/19/23 20:18
11/17/23 15:15
11/27/23
MDL
NA
NA
--
NA
Sample Depth:
Serial_No:11272318:05
Page 6 of 19
FF
EFFLUENTClient ID:
11/16/23 11:30Date Collected:
11/16/23Date Received:
Parameter Result
Dilution
Factor
Matrix:Water
BREWSTER, MASample Location:
L2368339-02Lab ID:
Qualifier Units RL
SAMPLE RESULTS
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2368339
Field Prep:
Date
Analyzed
Analytical
Method Analyst
Not Specified
General Chemistry - Westborough Lab
Solids, Total Suspended
Nitrogen, Ammonia
Nitrogen, Nitrite
Nitrogen, Nitrate
Nitrogen, Total Kjeldahl
BOD, 5 day
Oil & Grease, Hem-Grav
ND
1.02
ND
12.
2.42
ND
ND
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
1
1
1
5
2
1
.9
5.0
0.075
0.050
0.50
0.600
2.0
3.6
11/21/23 07:09
11/21/23 21:36
11/17/23 05:58
11/17/23 06:08
11/21/23 18:53
11/22/23 12:00
11/22/23 15:59
121,2540D
121,4500NH3-BH
44,353.2
44,353.2
121,4500NH3-H
121,5210B
140,1664B
MRS
AT
KAF
KAF
AT
MKT
JGM
Date
Prepared
-
11/19/23 20:18
-
-
11/19/23 23:52
11/17/23 15:15
11/22/23 13:01
11/27/23
MDL
NA
--
--
--
--
NA
--
Sample Depth:
Serial_No:11272318:05
Page 7 of 19
FF
Parameter Result
Dilution
FactorQualifierUnitsRL
Method Blank Analysis
Batch Quality Control
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2368339
Date
Analyzed
Analytical
Method Analyst
Date
Prepared
11/27/23
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Nitrogen, Total Kjeldahl
Nitrogen, Ammonia
Solids, Total
Solids, Total Suspended
Oil & Grease, Hem-Grav
Solids, Total Suspended
ND
ND
ND
ND
ND
ND
ND
ND
ND
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
1
1
1
1
1
1
1
1
1
0.050
0.10
2.0
0.300
0.075
10
5.0
4.0
5.0
11/17/23 03:25
11/17/23 03:30
11/22/23 12:00
11/21/23 18:41
11/21/23 21:18
11/21/23 05:06
11/21/23 07:09
11/22/23 14:38
11/22/23 20:56
44,353.2
44,353.2
121,5210B
121,4500NH3-H
121,4500NH3-BH
121,2540B
121,2540D
140,1664B
121,2540D
KAF
KAF
MKT
AT
AT
DEW
MRS
JGM
REM
-
-
11/17/23 15:15
11/19/23 23:52
11/19/23 20:18
-
-
11/22/23 13:01
-
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1853477-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1853481-1
General Chemistry - Westborough Lab for sample(s): 01-02 Batch: WG1853807-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1854242-1
General Chemistry - Westborough Lab for sample(s): 01-02 Batch: WG1854310-1
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1854947-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1855029-1
General Chemistry - Westborough Lab for sample(s): 02 Batch: WG1855735-1
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1855878-1
MDL
--
--
NA
--
--
NA
NA
--
NA
Serial_No:11272318:05
Page 8 of 19
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Nitrogen, Total Kjeldahl
Nitrogen, Ammonia
Solids, Total
Solids, Total Suspended
102
96
100
115
105
101
76
-
-
-
-
-
-
-
90-110
90-110
85-115
78-122
80-120
80-120
80-120
-
-
-
-
-
-
-
20
20
20
Parameter
LCS
%Recovery
LCSD
%Recovery
%Recovery
Limits RPD RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1853477-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1853481-2
General Chemistry - Westborough Lab Associated sample(s): 01-02 Batch: WG1853807-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1854242-2
General Chemistry - Westborough Lab Associated sample(s): 01-02 Batch: WG1854310-2
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1854947-2
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1855029-2
Lab Control Sample Analysis
Batch Quality ControlProject Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2368339
11/27/23
Qual Qual
Q
Qual
Serial_No:11272318:05
Page 9 of 19
Oil & Grease, Hem-Grav
Solids, Total Suspended
79
101
-
-
78-114
80-120
-
-
18
Parameter
LCS
%Recovery
LCSD
%Recovery
%Recovery
Limits RPD RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 02 Batch: WG1855735-2
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1855878-2
Lab Control Sample Analysis
Batch Quality ControlProject Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2368339
11/27/23
Serial_No:11272318:05
Page 10 of 19
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Nitrogen, Total Kjeldahl
Nitrogen, Ammonia
Oil & Grease, Hem-Grav
Oil & Grease, Hem-Grav
ND
12
ND
ND
620
ND
ND
4.2
16
89
5.96
655
32
32
105
100
89
74
88
85
85
-
-
-
-
-
-
-
-
-
-
-
-
-
-
80-120
83-113
50-145
77-111
80-120
78-114
78-114
-
-
-
-
-
-
-
20
6
35
24
20
18
18
Parameter
Native
Sample
MS
Found
MS
%Recovery
MSD
Found
MSD
%Recovery
Recovery
Limits RPD
RPD
Limits
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1853477-4 QC Sample: L2368339-02 Client ID: EFFLUENT
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1853481-4 QC Sample: L2368339-02 Client ID: EFFLUENT
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1853807-4 QC Sample: L2368222-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1854242-4 QC Sample: L2368371-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1854310-4 QC Sample: L2368391-02 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1855735-4 QC Sample: L2367637-02 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1855735-6 QC Sample: L2362960-99 Client ID: MS Sample
4
4
100
8
40
37.7
37.7
MS
Added
Matrix Spike Analysis
Batch Quality Control
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2368339
11/27/23
Qual
Q
Qual Qual
Serial_No:11272318:05
Page 11 of 19
Nitrogen, Nitrite
Nitrogen, Nitrate
BOD, 5 day
Nitrogen, Total Kjeldahl
Nitrogen, Ammonia
Solids, Total
Oil & Grease, Hem-Grav
Solids, Total Suspended
Solids, Total Suspended
ND
12
ND
ND
620
320
ND
730
41
ND
12
ND
ND
573
350
ND
730
41
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
mg/l
NC
0
NC
NC
8
9
NC
0
0
20
6
35
24
20
16
18
32
32
Units RPDParameterNative Sample Duplicate Sample RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1853477-3 QC Sample: L2368339-02 Client ID: EFFLUENT
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1853481-3 QC Sample: L2368339-02 Client ID: EFFLUENT
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1853807-3 QC Sample: L2368222-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1854242-3 QC Sample: L2368371-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01-02 QC Batch ID: WG1854310-3 QC Sample: L2368391-02 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1854947-3 QC Sample: L2367614-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 02 QC Batch ID: WG1855735-3 QC Sample: L2367637-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1855878-3 QC Sample: L2368386-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1855878-4 QC Sample: L2368663-01 Client ID: DUP Sample
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
L2368339Lab Number:
Report Date:
Lab Duplicate Analysis
Batch Quality Control
11/27/23
Qual
Serial_No:11272318:05
Page 12 of 19
*Values in parentheses indicate holding time in days
L2368339-01A
L2368339-01B
L2368339-01C
L2368339-02A
L2368339-02B
L2368339-02C
L2368339-02D
L2368339-02E
Plastic 500ml H2SO4 preserved
Plastic 950ml unpreserved
Plastic 950ml unpreserved
Plastic 500ml H2SO4 preserved
Plastic 950ml unpreserved
Plastic 950ml unpreserved
Amber 1000ml HCl preserved
Amber 1000ml HCl preserved
A
A
A
C
C
C
C
C
<2
7
7
<2
7
7
NA
NA
5.3
5.3
5.3
2.2
2.2
2.2
2.2
2.2
Y
Y
Y
Y
Y
Y
Y
Y
Absent
Absent
Absent
Absent
Absent
Absent
Absent
Absent
A
C
Absent
Absent
Cooler Custody Seal
Cooler Information
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
NH3-4500(28)
TSC-2540(7),BOD-5210(2)
TSS-2540(7)
TKN-4500(28),NH3-4500(28)
NO2-353(2),NO3-353(2),BOD-5210(2)
TSS-2540(7)
OG-1664(28)
OG-1664(28)
Project Name:
Project Number:
L2368339Lab Number:
Report Date:
Sample Receipt and Container Information
Container ID Container Type Cooler
Temp
deg C Pres Seal
Container Information
Analysis(*)
11/27/23
Were project specific reporting limits specified?YES
<2
7
7
<2
7
7
Frozen
Date/Time
Final
pH
Initial
pH
Serial_No:11272318:05
Page 13 of 19
Report Format:Data Usability Report
GLOSSARY
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700 11/27/23
Acronyms
DL
EDL
EMPC
EPA
LCS
LCSD
LFB
LOD
LOQ
MDL
MS
MSD
NA
NC
NDPA/DPA
NI
NP
NR
RL
RPD
SRM
STLP
TEF
TEQ
TIC
Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated values, when
those target analyte concentrations are quantified below the limit of quantitation (LOQ). The DL includes any adjustments
from dilutions, concentrations or moisture content, where applicable. (DoD report formats only.)
Estimated Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated
values, when those target analyte concentrations are quantified below the reporting limit (RL). The EDL includes any
adjustments from dilutions, concentrations or moisture content, where applicable. The use of EDLs is specific to the analysis
of PAHs using Solid-Phase Microextraction (SPME).
Estimated Maximum Possible Concentration: The concentration that results from the signal present at the retention time of an
analyte when the ions meet all of the identification criteria except the ion abundance ratio criteria. An EMPC is a worst-case
estimate of the concentration.
Environmental Protection Agency.
Laboratory Control Sample: A sample matrix, free from the analytes of interest, spiked with verified known amounts of
analytes or a material containing known and verified amounts of analytes.
Laboratory Control Sample Duplicate: Refer to LCS.
Laboratory Fortified Blank: A sample matrix, free from the analytes of interest, spiked with verified known amounts of
analytes or a material containing known and verified amounts of analytes.
Limit of Detection: This value represents the level to which a target analyte can reliably be detected for a specific analyte in a
specific matrix by a specific method. The LOD includes any adjustments from dilutions, concentrations or moisture content,
where applicable. (DoD report formats only.)
Limit of Quantitation: The value at which an instrument can accurately measure an analyte at a specific concentration. The
LOQ includes any adjustments from dilutions, concentrations or moisture content, where applicable. (DoD report formats
only.)
Limit of Quantitation: The value at which an instrument can accurately measure an analyte at a specific concentration. The
LOQ includes any adjustments from dilutions, concentrations or moisture content, where applicable. (DoD report formats
only.)
Method Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated
values, when those target analyte concentrations are quantified below the reporting limit (RL). The MDL includes any
adjustments from dilutions, concentrations or moisture content, where applicable.
Matrix Spike Sample: A sample prepared by adding a known mass of target analyte to a specified amount of matrix sample for
which an independent estimate of target analyte concentration is available. For Method 332.0, the spike recovery is calculated
using the native concentration, including estimated values.
Matrix Spike Sample Duplicate: Refer to MS.
Not Applicable.
Not Calculated: Term is utilized when one or more of the results utilized in the calculation are non-detect at the parameter's
reporting unit.
N-Nitrosodiphenylamine/Diphenylamine.
Not Ignitable.
Non-Plastic: Term is utilized for the analysis of Atterberg Limits in soil.
No Results: Term is utilized when 'No Target Compounds Requested' is reported for the analysis of Volatile or Semivolatile
Organic TIC only requests.
Reporting Limit: The value at which an instrument can accurately measure an analyte at a specific concentration. The RL
includes any adjustments from dilutions, concentrations or moisture content, where applicable.
Relative Percent Difference: The results from matrix and/or matrix spike duplicates are primarily designed to assess the
precision of analytical results in a given matrix and are expressed as relative percent difference (RPD). Values which are less
than five times the reporting limit for any individual parameter are evaluated by utilizing the absolute difference between the
values; although the RPD value will be provided in the report.
Standard Reference Material: A reference sample of a known or certified value that is of the same or similar matrix as the
associated field samples.
Semi-dynamic Tank Leaching Procedure per EPA Method 1315.
Toxic Equivalency Factors: The values assigned to each dioxin and furan to evaluate their toxicity relative to 2,3,7,8-TCDD.
Toxic Equivalent: The measure of a sample's toxicity derived by multiplying each dioxin and furan by its corresponding TEF
and then summing the resulting values.
Tentatively Identified Compound: A compound that has been identified to be present and is not part of the target compound
list (TCL) for the method and/or program. All TICs are qualitatively identified and reported as estimated concentrations.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Serial_No:11272318:05
Page 14 of 19
Report Format:Data Usability Report
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700 11/27/23
Terms
Analytical Method: Both the document from which the method originates and the analytical reference method. (Example: EPA 8260B is
shown as 1,8260B.) The codes for the reference method documents are provided in the References section of the Addendum.
Chlordane: The target compound Chlordane (CAS No. 57-74-9) is reported for GC ECD analyses. Per EPA,this compound "refers to a
mixture of chlordane isomers, other chlorinated hydrocarbons and numerous other components." (Reference: USEPA Toxicological Review
of Chlordane, In Support of Summary Information on the Integrated Risk Information System (IRIS), December 1997.)
Difference: With respect to Total Oxidizable Precursor (TOP) Assay analysis, the difference is defined as the Post-Treatment value minus the
Pre-Treatment value.
Final pH: As it pertains to Sample Receipt & Container Information section of the report, Final pH reflects pH of container determined after
adjustment at the laboratory, if applicable. If no adjustment required, value reflects Initial pH.
Frozen Date/Time: With respect to Volatile Organics in soil, Frozen Date/Time reflects the date/time at which associated Reagent Water-
preserved vials were initially frozen. Note: If frozen date/time is beyond 48 hours from sample collection, value will be reflected in 'bold'.
Gasoline Range Organics (GRO): Gasoline Range Organics (GRO) results include all chromatographic peaks eluting from Methyl tert butyl
ether through Naphthalene, with the exception of GRO analysis in support of State of Ohio programs, which includes all chromatographic
peaks eluting from Hexane through Dodecane.
Initial pH: As it pertains to Sample Receipt & Container Information section of the report, Initial pH reflects pH of container determined upon
receipt, if applicable.
PAH Total: With respect to Alkylated PAH analyses, the 'PAHs, Total' result is defined as the summation of results for all or a subset of the
following compounds: Naphthalene, C1-C4 Naphthalenes, 2-Methylnaphthalene, 1-Methylnaphthalene, Biphenyl, Acenaphthylene,
Acenaphthene, Fluorene, C1-C3 Fluorenes, Phenanthrene, C1-C4 Phenanthrenes/Anthracenes, Anthracene, Fluoranthene, Pyrene, C1-C4
Fluoranthenes/Pyrenes, Benz(a)anthracene, Chrysene, C1-C4 Chrysenes, Benzo(b)fluoranthene, Benzo(j)+(k)fluoranthene, Benzo(e)pyrene,
Benzo(a)pyrene, Perylene, Indeno(1,2,3-cd)pyrene, Dibenz(ah)+(ac)anthracene, Benzo(g,h,i)perylene. If a 'Total' result is requested, the
results of its individual components will also be reported.
PFAS Total: With respect to PFAS analyses, the 'PFAS, Total (5)' result is defined as the summation of results for: PFHpA, PFHxS, PFOA,
PFNA and PFOS. In addition, the 'PFAS, Total (6)' result is defined as the summation of results for: PFHpA, PFHxS, PFOA, PFNA, PFDA
and PFOS. For MassDEP DW compliance analysis only, the 'PFAS, Total (6)' result is defined as the summation of results at or above the
RL. Note: If a 'Total' result is requested, the results of its individual components will also be reported.
Total: With respect to Organic analyses, a 'Total' result is defined as the summation of results for individual isomers or Aroclors. If a 'Total'
result is requested, the results of its individual components will also be reported. This is applicable to 'Total' results for methods 8260, 8081
and 8082.
Data Qualifiers
A
B
C
D
E
F
G
H
I
J
M
-
-
-
-
-
-
-
-
-
-
-
Spectra identified as "Aldol Condensates" are byproducts of the extraction/concentration procedures when acetone is introduced in
the process.
The analyte was detected above the reporting limit in the associated method blank. Flag only applies to associated field samples that
have detectable concentrations of the analyte at less than ten times (10x) the concentration found in the blank. For MCP-related
projects, flag only applies to associated field samples that have detectable concentrations of the analyte at less than ten times (10x)
the concentration found in the blank. For DOD-related projects, flag only applies to associated field samples that have detectable
concentrations of the analyte at less than ten times (10x) the concentration found in the blank AND the analyte was detected above
one-half the reporting limit (or above the reporting limit for common lab contaminants) in the associated method blank. For NJ-
Air-related projects, flag only applies to associated field samples that have detectable concentrations of the analyte above the
reporting limit. For NJ-related projects (excluding Air), flag only applies to associated field samples that have detectable
concentrations of the analyte, which was detected above the reporting limit in the associated method blank or above five times the
reporting limit for common lab contaminants (Phthalates, Acetone, Methylene Chloride, 2-Butanone).
Co-elution: The target analyte co-elutes with a known lab standard (i.e. surrogate, internal standards, etc.) for co-extracted
analyses.
Concentration of analyte was quantified from diluted analysis. Flag only applies to field samples that have detectable concentrations
of the analyte.
Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
The ratio of quantifier ion response to qualifier ion response falls outside of the laboratory criteria. Results are considered to be an
estimated maximum concentration.
The concentration may be biased high due to matrix interferences (i.e, co-elution) with non-target compound(s). The result should
be considered estimated.
The analysis of pH was performed beyond the regulatory-required holding time of 15 minutes from the time of sample collection.
The lower value for the two columns has been reported due to obvious interference.
Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
Reporting Limit (RL) exceeds the MCP CAM Reporting Limit for this analyte.
1 The reference for this analyte should be considered modified since this analyte is absent from the target analyte list of the
original method.
-
Footnotes
Serial_No:11272318:05
Page 15 of 19
Report Format:Data Usability Report
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700 11/27/23
Data Qualifiers
ND
NJ
P
Q
R
RE
S
V
Z
-
-
-
-
-
-
-
-
-
Not detected at the reporting limit (RL) for the sample.
Presumptive evidence of compound. This represents an estimated concentration for Tentatively Identified Compounds (TICs), where
the identification is based on a mass spectral library search.
The RPD between the results for the two columns exceeds the method-specified criteria.
The quality control sample exceeds the associated acceptance criteria. For DOD-related projects, LCS and/or Continuing Calibration
Standard exceedences are also qualified on all associated sample results. Note: This flag is not applicable for matrix spike recoveries
when the sample concentration is greater than 4x the spike added or for batch duplicate RPD when the sample concentrations are less
than 5x the RL. (Metals only.)
Analytical results are from sample re-analysis.
Analytical results are from sample re-extraction.
Analytical results are from modified screening analysis.
The surrogate associated with this target analyte has a recovery outside the QC acceptance limits. (Applicable to MassDEP DW
Compliance samples only.)
The batch matrix spike and/or duplicate associated with this target analyte has a recovery/RPD outside the QC acceptance limits.
(Applicable to MassDEP DW Compliance samples only.)
Serial_No:11272318:05
Page 16 of 19
Alpha Analytical performs services with reasonable care and diligence normal to the analytical testing
laboratory industry. In the event of an error, the sole and exclusive responsibility of Alpha Analytical
shall be to re-perform the work at it's own expense. In no event shall Alpha Analytical be held liable
for any incidental, consequential or special damages, including but not limited to, damages in any way
connected with the use of, interpretation of, information or analysis provided by Alpha Analytical.
We strongly urge our clients to comply with EPA protocol regarding sample volume, preservation, cooling,
containers, sampling procedures, holding time and splitting of samples in the field.
LIMITATION OF LIABILITIES
44
121
140
Methods for the Determination of Inorganic Substances in Environmental Samples,
EPA/600/R-93/100, August 1993.
Standard Methods for the Examination of Water and Wastewater. APHA-AWWA-WEF.
Standard Methods Online.
Method 1664,Revision B: N-Hexane Extractable Material (HEM; Oil & Grease) and
Silica Gel Treated N-Hexane Extractable Material (SGT-HEM; Non-polar Material) by
Extraction and Gravimetry, EPA-821-R-10-001, February 2010.
Project Name:
Project Number:
Lab Number:
Report Date:
L2368339MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
REFERENCES
11/27/23
Serial_No:11272318:05
Page 17 of 19
Alpha Analytical, Inc.ID No.:17873
Facility: Company-wide Revision 20
Department: Quality Assurance Published Date: 6/16/2023 4:52:28 PM
Title: Certificate/Approval Program Summary Page 1 of 1
Document Type: Form Pre-Qualtrax Document ID: 08-113
Certification Information
The following analytes are not included in our Primary NELAP Scope of Accreditation:
Westborough Facility
EPA 624.1: m/p-xylene, o-xylene, Naphthalene
EPA 625.1: alpha-Terpineol
EPA 8260D: NPW: 1,2,4,5-Tetramethylbenzene; 4-Ethyltoluene, Azobenzene; SCM: Iodomethane (methyl iodide), 1,2,4,5-Tetramethylbenzene; 4-
Ethyltoluene.
EPA 8270E: NPW: Dimethylnaphthalene,1,4-Diphenylhydrazine, alpha-Terpineol; SCM: Dimethylnaphthalene,1,4-Diphenylhydrazine.
SM4500: NPW: Amenable Cyanide; SCM: Total Phosphorus, TKN, NO2, NO3.
Mansfield Facility
SM 2540D: TSS.
EPA TO-15: Halothane, 2,4,4-Trimethyl-2-pentene, 2,4,4-Trimethyl-1-pentene, Thiophene, 2-Methylthiophene,
3-Methylthiophene, 2-Ethylthiophene, 1,2,3-Trimethylbenzene, Indan, Indene, 1,2,4,5-Tetramethylbenzene, Benzothiophene, 1-Methylnaphthalene.
Biological Tissue Matrix: EPA 3050B
The following analytes are included in our Massachusetts DEP Scope of Accreditation
Westborough Facility:
Drinking Water
EPA 300.0: Chloride, Nitrate-N, Fluoride, Sulfate; EPA 353.2: Nitrate-N, Nitrite-N; SM4500NO3-F: Nitrate-N, Nitrite-N; SM4500F-C, SM4500CN-CE,
EPA 180.1, SM2130B, SM4500Cl-D, SM2320B, SM2540C, SM4500H-B, SM4500NO2-B
EPA 524.2: THMs and VOCs; EPA 504.1: EDB, DBCP.
Microbiology: SM9215B; SM9223-P/A, SM9223B-Colilert-QT,SM9222D.
Non-Potable Water
SM4500H,B, EPA 120.1, SM2510B, SM2540C, SM2320B, SM4500CL-E, SM4500F-BC, SM4500NH3-BH: Ammonia-N and Kjeldahl-N, EPA 350.1:
Ammonia-N, LACHAT 10-107-06-1-B: Ammonia-N, EPA 351.1, SM4500NO3-F, EPA 353.2: Nitrate-N, SM4500P-E, SM4500P-B, E, SM4500SO4-E,
SM5220D, EPA 410.4, SM5210B, SM5310C, SM4500CL-D, EPA 1664, EPA 420.1, SM4500-CN-CE, SM2540D, EPA 300: Chloride, Sulfate, Nitrate.
EPA 624.1: Volatile Halocarbons & Aromatics,
EPA 608.3: Chlordane, Toxaphene, Aldrin, alpha-BHC, beta-BHC, gamma-BHC, delta-BHC, Dieldrin, DDD, DDE, DDT, Endosulfan I, Endosulfan II,
Endosulfan sulfate, Endrin, Endrin Aldehyde, Heptachlor, Heptachlor Epoxide, PCBs
EPA 625.1: SVOC (Acid/Base/Neutral Extractables).
Microbiology: SM9223B-Colilert-QT; Enterolert-QT, SM9221E, EPA 1600, EPA 1603, SM9222D.
Mansfield Facility:
Drinking Water
EPA 200.7: Al, Ba, Cd, Cr, Cu, Fe, Mn, Ni, Na, Ag, Ca, Zn. EPA 200.8: Al, Sb, As, Ba, Be, Cd, Cr, Cu, Pb, Mn, Ni, Se, Ag, TL, Zn. EPA 245.1 Hg.
EPA 522, EPA 537.1.
Non-Potable Water
EPA 200.7: Al, Sb, As, Be, Cd, Ca, Cr, Co, Cu, Fe, Pb, Mg, Mn, Mo, Ni, K, Se, Ag, Na, Sr, TL, Ti, V, Zn.
EPA 200.8: Al, Sb, As, Be, Cd, Cr, Cu, Fe, Pb, Mn, Ni, K, Se, Ag, Na, TL, Zn.
EPA 245.1 Hg.
SM2340B
For a complete listing of analytes and methods, please contact your Alpha Project Manager.
Serial_No:11272318:05
Page 18 of 19
Serial_No:11272318:05
Page 19 of 19
L2371568
Bennett Environmental Associates
K10842DA.S.WW.700
MAPLEWOOD AT BREWSTER
Client:
Project Name:
Project Number:
12/11/23
Eight Walkup Drive, Westborough, MA 01581-1019
Lab Number:
Report Date:
508-898-9220 (Fax) 508-898-9193 800-624-9220 - www.alphalab.com
1573 Main Street
Brewster, MA 02631
Samantha FarrenkopfATTN:
ANALYTICAL REPORT
Certifications & Approvals: MA (M-MA086), NH NELAP (2064), CT (PH-0826), IL (200077), IN (C-MA-03), KY (KY98045), ME (MA00086), MD
(348), NJ (MA935), NY (11148), NC (25700/666), OH (CL108), OR (MA-1316), PA (68-03671), RI (LAO00065), TX (T104704476), VT (VT-0935),
VA (460195), USDA (Permit #525-23-122-91930).
(508) 896-1706Phone:
The original project report/data package is held by Alpha Analytical. This report/data package is paginated and should be reproduced only in its
entirety. Alpha Analytical holds no responsibility for results and/or data that are not consistent with the original.
Serial_No:12112319:27
Page 1 of 16
L2371568-01
Alpha
Sample ID
EFFLUENT RESAMPLE
Client ID
BREWSTER, MA
Sample
Location
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2371568
12/11/23
12/05/23 12:00
Collection
Date/TimeMatrix Receive Date
WATER 12/05/23
Serial_No:12112319:27
Page 2 of 16
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
Lab Number:
Report Date:
L2371568
12/11/23
Case Narrative
I, the undersigned, attest under the pains and penalties of perjury that, to the best of my knowledge and
belief and based upon my personal inquiry of those responsible for providing the information contained
in this analytical report, such information is accurate and complete. This certificate of analysis is not
complete unless this page accompanies any and all pages of this report.
Authorized Signature:
Title: Technical Director/Representative Date: 12/11/23
The samples were received in accordance with the Chain of Custody and no significant deviations were encountered during the preparation
or analysis unless otherwise noted. Sample Receipt, Container Information, and the Chain of Custody are located at the back of the report.
Results contained within this report relate only to the samples submitted under this Alpha Lab Number and meet NELAP requirements for all
NELAP accredited parameters unless otherwise noted in the following narrative. The data presented in this report is organized by parameter
(i.e. VOC, SVOC, etc.). Sample specific Quality Control data (i.e. Surrogate Spike Recovery) is reported at the end of the target analyte list
for each individual sample, followed by the Laboratory Batch Quality Control at the end of each parameter. Tentatively Identified
Compounds (TICs), if requested, are reported for compounds identified to be present and are not part of the method/program Target
Compound List, even if only a subset of the TCL are being reported. If a sample was re-analyzed or re-extracted due to a required quality
control corrective action and if both sets of data are reported, the Laboratory ID of the re-analysis or re-extraction is designated with an "R"
or "RE", respectively.
When multiple Batch Quality Control elements are reported (e.g. more than one LCS), the associated samples for each element are noted in
the grey shaded header line of each data table. Any Laboratory Batch, Sample Specific % recovery or RPD value that is outside the listed
Acceptance Criteria is bolded in the report. In reference to questions H (CAM) or 4 (RCP) when "NO" is checked, the performance criteria
for CAM and RCP methods allow for some quality control failures to occur and still be within method compliance. In these instances, the
specific failure is not narrated but noted in the associated QC Outlier Summary Report, located directly after the Case Narrative. QC
information is also incorporated in the Data Usability Assessment table (Format 11) of our Data Merger tool, where it can be reviewed in
conjunction with the sample result, associated regulatory criteria and any associated data usability implications.
Soil/sediments, solids and tissues are reported on a dry weight basis unless otherwise noted. Definitions of all data qualifiers and acronyms
used in this report are provided in the Glossary located at the back of the report.
HOLD POLICY - For samples submitted on hold, Alpha's policy is to hold samples (with the exception of Air canisters) free of charge for 21
calendar days from the date the project is completed. After 21 calendar days, we will dispose of all samples submitted including those put
on hold unless you have contacted your Alpha Project Manager and made arrangements for Alpha to continue to hold the samples. Air
canisters will be disposed after 3 business days from the date the project is completed.
Please contact Project Management at 800-624-9220 with any questions.
Serial_No:12112319:27
Page 3 of 16
INORGANICS
&
MISCELLANEOUS
Serial_No:12112319:27
Page 4 of 16
FF
EFFLUENT RESAMPLEClient ID:
12/05/23 12:00Date Collected:
12/05/23Date Received:
Parameter Result
Dilution
Factor
Matrix:Water
BREWSTER, MASample Location:
L2371568-01Lab ID:
Qualifier Units RL
SAMPLE RESULTS
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2371568
Field Prep:
Date
Analyzed
Analytical
Method Analyst
Not Specified
General Chemistry - Westborough Lab
Nitrogen, Nitrite
Nitrogen, Nitrate
Nitrogen, Total Kjeldahl
ND
0.22
2.37
mg/l
mg/l
mg/l
1
1
1
0.050
0.10
0.300
12/07/23 07:19
12/07/23 07:19
12/08/23 13:43
44,353.2
44,353.2
121,4500NH3-H
KAF
KAF
KEP
Date
Prepared
-
-
12/06/23 17:29
12/11/23
MDL
--
--
--
Sample Depth:
Serial_No:12112319:27
Page 5 of 16
FF
Parameter Result
Dilution
FactorQualifierUnitsRL
Method Blank Analysis
Batch Quality Control
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2371568
Date
Analyzed
Analytical
Method Analyst
Date
Prepared
12/11/23
Nitrogen, Total Kjeldahl
Nitrogen, Nitrite
Nitrogen, Nitrate
ND
ND
ND
mg/l
mg/l
mg/l
1
1
1
0.300
0.050
0.10
12/08/23 13:00
12/07/23 03:45
12/07/23 04:02
121,4500NH3-H
44,353.2
44,353.2
KEP
KAF
KAF
12/06/23 17:29
-
-
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1860488-1
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1860745-1
General Chemistry - Westborough Lab for sample(s): 01 Batch: WG1860753-1
MDL
--
--
--
Serial_No:12112319:27
Page 6 of 16
Nitrogen, Total Kjeldahl
Nitrogen, Nitrite
Nitrogen, Nitrate
98
100
106
-
-
-
78-122
90-110
90-110
-
-
-
20
Parameter
LCS
%Recovery
LCSD
%Recovery
%Recovery
Limits RPD RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1860488-2
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1860745-2
General Chemistry - Westborough Lab Associated sample(s): 01 Batch: WG1860753-2
Lab Control Sample Analysis
Batch Quality ControlProject Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2371568
12/11/23
Qual Qual Qual
Serial_No:12112319:27
Page 7 of 16
Nitrogen, Total Kjeldahl
Nitrogen, Nitrite
Nitrogen, Nitrate
2.68
ND
16
9.71
4.5
20
88
112
102
-
-
-
-
-
-
77-111
80-120
83-113
-
-
-
24
20
6
Parameter
Native
Sample
MS
Found
MS
%Recovery
MSD
Found
MSD
%Recovery
Recovery
Limits RPD
RPD
Limits
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1860488-4 QC Sample: L2371537-02 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1860745-4 QC Sample: L2371527-01 Client ID: MS Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1860753-4 QC Sample: L2371527-01 Client ID: MS Sample
8
4
4
MS
Added
Matrix Spike Analysis
Batch Quality Control
Project Name:
Project Number:
Lab Number:
Report Date:
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
L2371568
12/11/23
Qual Qual Qual
Serial_No:12112319:27
Page 8 of 16
Nitrogen, Total Kjeldahl
Nitrogen, Nitrite
Nitrogen, Nitrate
2.68
ND
16
3.16
ND
16
mg/l
mg/l
mg/l
16
NC
0
24
20
6
Units RPDParameterNative Sample Duplicate Sample RPD Limits
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1860488-3 QC Sample: L2371537-02 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1860745-3 QC Sample: L2371527-01 Client ID: DUP Sample
General Chemistry - Westborough Lab Associated sample(s): 01 QC Batch ID: WG1860753-3 QC Sample: L2371527-01 Client ID: DUP Sample
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
Project Name:
Project Number:
L2371568Lab Number:
Report Date:
Lab Duplicate Analysis
Batch Quality Control
12/11/23
Qual
Serial_No:12112319:27
Page 9 of 16
*Values in parentheses indicate holding time in days
L2371568-01A
L2371568-01B
Plastic 500ml H2SO4 preserved
Plastic 950ml unpreserved
B
B
<2
7
4.2
4.2
Y
Y
Absent
Absent
B Absent
Cooler Custody Seal
Cooler Information
MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
TKN-4500(28)
NO2-353(2),NO3-353(2)
Project Name:
Project Number:
L2371568Lab Number:
Report Date:
Sample Receipt and Container Information
Container ID Container Type Cooler
Temp
deg C Pres Seal
Container Information
Analysis(*)
12/11/23
Were project specific reporting limits specified?YES
<2
7
Frozen
Date/Time
Final
pH
Initial
pH
Serial_No:12112319:27
Page 10 of 16
Report Format:Data Usability Report
GLOSSARY
Project Name:
Project Number:
Lab Number:
Report Date:
L2371568MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700 12/11/23
Acronyms
DL
EDL
EMPC
EPA
LCS
LCSD
LFB
LOD
LOQ
MDL
MS
MSD
NA
NC
NDPA/DPA
NI
NP
NR
RL
RPD
SRM
STLP
TEF
TEQ
TIC
Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated values, when
those target analyte concentrations are quantified below the limit of quantitation (LOQ). The DL includes any adjustments
from dilutions, concentrations or moisture content, where applicable. (DoD report formats only.)
Estimated Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated
values, when those target analyte concentrations are quantified below the reporting limit (RL). The EDL includes any
adjustments from dilutions, concentrations or moisture content, where applicable. The use of EDLs is specific to the analysis
of PAHs using Solid-Phase Microextraction (SPME).
Estimated Maximum Possible Concentration: The concentration that results from the signal present at the retention time of an
analyte when the ions meet all of the identification criteria except the ion abundance ratio criteria. An EMPC is a worst-case
estimate of the concentration.
Environmental Protection Agency.
Laboratory Control Sample: A sample matrix, free from the analytes of interest, spiked with verified known amounts of
analytes or a material containing known and verified amounts of analytes.
Laboratory Control Sample Duplicate: Refer to LCS.
Laboratory Fortified Blank: A sample matrix, free from the analytes of interest, spiked with verified known amounts of
analytes or a material containing known and verified amounts of analytes.
Limit of Detection: This value represents the level to which a target analyte can reliably be detected for a specific analyte in a
specific matrix by a specific method. The LOD includes any adjustments from dilutions, concentrations or moisture content,
where applicable. (DoD report formats only.)
Limit of Quantitation: The value at which an instrument can accurately measure an analyte at a specific concentration. The
LOQ includes any adjustments from dilutions, concentrations or moisture content, where applicable. (DoD report formats
only.)
Limit of Quantitation: The value at which an instrument can accurately measure an analyte at a specific concentration. The
LOQ includes any adjustments from dilutions, concentrations or moisture content, where applicable. (DoD report formats
only.)
Method Detection Limit: This value represents the level to which target analyte concentrations are reported as estimated
values, when those target analyte concentrations are quantified below the reporting limit (RL). The MDL includes any
adjustments from dilutions, concentrations or moisture content, where applicable.
Matrix Spike Sample: A sample prepared by adding a known mass of target analyte to a specified amount of matrix sample for
which an independent estimate of target analyte concentration is available. For Method 332.0, the spike recovery is calculated
using the native concentration, including estimated values.
Matrix Spike Sample Duplicate: Refer to MS.
Not Applicable.
Not Calculated: Term is utilized when one or more of the results utilized in the calculation are non-detect at the parameter's
reporting unit.
N-Nitrosodiphenylamine/Diphenylamine.
Not Ignitable.
Non-Plastic: Term is utilized for the analysis of Atterberg Limits in soil.
No Results: Term is utilized when 'No Target Compounds Requested' is reported for the analysis of Volatile or Semivolatile
Organic TIC only requests.
Reporting Limit: The value at which an instrument can accurately measure an analyte at a specific concentration. The RL
includes any adjustments from dilutions, concentrations or moisture content, where applicable.
Relative Percent Difference: The results from matrix and/or matrix spike duplicates are primarily designed to assess the
precision of analytical results in a given matrix and are expressed as relative percent difference (RPD). Values which are less
than five times the reporting limit for any individual parameter are evaluated by utilizing the absolute difference between the
values; although the RPD value will be provided in the report.
Standard Reference Material: A reference sample of a known or certified value that is of the same or similar matrix as the
associated field samples.
Semi-dynamic Tank Leaching Procedure per EPA Method 1315.
Toxic Equivalency Factors: The values assigned to each dioxin and furan to evaluate their toxicity relative to 2,3,7,8-TCDD.
Toxic Equivalent: The measure of a sample's toxicity derived by multiplying each dioxin and furan by its corresponding TEF
and then summing the resulting values.
Tentatively Identified Compound: A compound that has been identified to be present and is not part of the target compound
list (TCL) for the method and/or program. All TICs are qualitatively identified and reported as estimated concentrations.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Serial_No:12112319:27
Page 11 of 16
Report Format:Data Usability Report
Project Name:
Project Number:
Lab Number:
Report Date:
L2371568MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700 12/11/23
Terms
Analytical Method: Both the document from which the method originates and the analytical reference method. (Example: EPA 8260B is
shown as 1,8260B.) The codes for the reference method documents are provided in the References section of the Addendum.
Chlordane: The target compound Chlordane (CAS No. 57-74-9) is reported for GC ECD analyses. Per EPA,this compound "refers to a
mixture of chlordane isomers, other chlorinated hydrocarbons and numerous other components." (Reference: USEPA Toxicological Review
of Chlordane, In Support of Summary Information on the Integrated Risk Information System (IRIS), December 1997.)
Difference: With respect to Total Oxidizable Precursor (TOP) Assay analysis, the difference is defined as the Post-Treatment value minus the
Pre-Treatment value.
Final pH: As it pertains to Sample Receipt & Container Information section of the report, Final pH reflects pH of container determined after
adjustment at the laboratory, if applicable. If no adjustment required, value reflects Initial pH.
Frozen Date/Time: With respect to Volatile Organics in soil, Frozen Date/Time reflects the date/time at which associated Reagent Water-
preserved vials were initially frozen. Note: If frozen date/time is beyond 48 hours from sample collection, value will be reflected in 'bold'.
Gasoline Range Organics (GRO): Gasoline Range Organics (GRO) results include all chromatographic peaks eluting from Methyl tert butyl
ether through Naphthalene, with the exception of GRO analysis in support of State of Ohio programs, which includes all chromatographic
peaks eluting from Hexane through Dodecane.
Initial pH: As it pertains to Sample Receipt & Container Information section of the report, Initial pH reflects pH of container determined upon
receipt, if applicable.
PAH Total: With respect to Alkylated PAH analyses, the 'PAHs, Total' result is defined as the summation of results for all or a subset of the
following compounds: Naphthalene, C1-C4 Naphthalenes, 2-Methylnaphthalene, 1-Methylnaphthalene, Biphenyl, Acenaphthylene,
Acenaphthene, Fluorene, C1-C3 Fluorenes, Phenanthrene, C1-C4 Phenanthrenes/Anthracenes, Anthracene, Fluoranthene, Pyrene, C1-C4
Fluoranthenes/Pyrenes, Benz(a)anthracene, Chrysene, C1-C4 Chrysenes, Benzo(b)fluoranthene, Benzo(j)+(k)fluoranthene, Benzo(e)pyrene,
Benzo(a)pyrene, Perylene, Indeno(1,2,3-cd)pyrene, Dibenz(ah)+(ac)anthracene, Benzo(g,h,i)perylene. If a 'Total' result is requested, the
results of its individual components will also be reported.
PFAS Total: With respect to PFAS analyses, the 'PFAS, Total (5)' result is defined as the summation of results for: PFHpA, PFHxS, PFOA,
PFNA and PFOS. In addition, the 'PFAS, Total (6)' result is defined as the summation of results for: PFHpA, PFHxS, PFOA, PFNA, PFDA
and PFOS. For MassDEP DW compliance analysis only, the 'PFAS, Total (6)' result is defined as the summation of results at or above the
RL. Note: If a 'Total' result is requested, the results of its individual components will also be reported.
Total: With respect to Organic analyses, a 'Total' result is defined as the summation of results for individual isomers or Aroclors. If a 'Total'
result is requested, the results of its individual components will also be reported. This is applicable to 'Total' results for methods 8260, 8081
and 8082.
Data Qualifiers
A
B
C
D
E
F
G
H
I
J
M
-
-
-
-
-
-
-
-
-
-
-
Spectra identified as "Aldol Condensates" are byproducts of the extraction/concentration procedures when acetone is introduced in
the process.
The analyte was detected above the reporting limit in the associated method blank. Flag only applies to associated field samples that
have detectable concentrations of the analyte at less than ten times (10x) the concentration found in the blank. For MCP-related
projects, flag only applies to associated field samples that have detectable concentrations of the analyte at less than ten times (10x)
the concentration found in the blank. For DOD-related projects, flag only applies to associated field samples that have detectable
concentrations of the analyte at less than ten times (10x) the concentration found in the blank AND the analyte was detected above
one-half the reporting limit (or above the reporting limit for common lab contaminants) in the associated method blank. For NJ-
Air-related projects, flag only applies to associated field samples that have detectable concentrations of the analyte above the
reporting limit. For NJ-related projects (excluding Air), flag only applies to associated field samples that have detectable
concentrations of the analyte, which was detected above the reporting limit in the associated method blank or above five times the
reporting limit for common lab contaminants (Phthalates, Acetone, Methylene Chloride, 2-Butanone).
Co-elution: The target analyte co-elutes with a known lab standard (i.e. surrogate, internal standards, etc.) for co-extracted
analyses.
Concentration of analyte was quantified from diluted analysis. Flag only applies to field samples that have detectable concentrations
of the analyte.
Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
The ratio of quantifier ion response to qualifier ion response falls outside of the laboratory criteria. Results are considered to be an
estimated maximum concentration.
The concentration may be biased high due to matrix interferences (i.e, co-elution) with non-target compound(s). The result should
be considered estimated.
The analysis of pH was performed beyond the regulatory-required holding time of 15 minutes from the time of sample collection.
The lower value for the two columns has been reported due to obvious interference.
Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
Reporting Limit (RL) exceeds the MCP CAM Reporting Limit for this analyte.
1 The reference for this analyte should be considered modified since this analyte is absent from the target analyte list of the
original method.
-
Footnotes
Serial_No:12112319:27
Page 12 of 16
Report Format:Data Usability Report
Project Name:
Project Number:
Lab Number:
Report Date:
L2371568MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700 12/11/23
Data Qualifiers
ND
NJ
P
Q
R
RE
S
V
Z
-
-
-
-
-
-
-
-
-
Not detected at the reporting limit (RL) for the sample.
Presumptive evidence of compound. This represents an estimated concentration for Tentatively Identified Compounds (TICs), where
the identification is based on a mass spectral library search.
The RPD between the results for the two columns exceeds the method-specified criteria.
The quality control sample exceeds the associated acceptance criteria. For DOD-related projects, LCS and/or Continuing Calibration
Standard exceedences are also qualified on all associated sample results. Note: This flag is not applicable for matrix spike recoveries
when the sample concentration is greater than 4x the spike added or for batch duplicate RPD when the sample concentrations are less
than 5x the RL. (Metals only.)
Analytical results are from sample re-analysis.
Analytical results are from sample re-extraction.
Analytical results are from modified screening analysis.
The surrogate associated with this target analyte has a recovery outside the QC acceptance limits. (Applicable to MassDEP DW
Compliance samples only.)
The batch matrix spike and/or duplicate associated with this target analyte has a recovery/RPD outside the QC acceptance limits.
(Applicable to MassDEP DW Compliance samples only.)
Serial_No:12112319:27
Page 13 of 16
Alpha Analytical performs services with reasonable care and diligence normal to the analytical testing
laboratory industry. In the event of an error, the sole and exclusive responsibility of Alpha Analytical
shall be to re-perform the work at it's own expense. In no event shall Alpha Analytical be held liable
for any incidental, consequential or special damages, including but not limited to, damages in any way
connected with the use of, interpretation of, information or analysis provided by Alpha Analytical.
We strongly urge our clients to comply with EPA protocol regarding sample volume, preservation, cooling,
containers, sampling procedures, holding time and splitting of samples in the field.
LIMITATION OF LIABILITIES
44
121
Methods for the Determination of Inorganic Substances in Environmental Samples,
EPA/600/R-93/100, August 1993.
Standard Methods for the Examination of Water and Wastewater. APHA-AWWA-WEF.
Standard Methods Online.
Project Name:
Project Number:
Lab Number:
Report Date:
L2371568MAPLEWOOD AT BREWSTER
K10842DA.S.WW.700
REFERENCES
12/11/23
Serial_No:12112319:27
Page 14 of 16
Alpha Analytical, Inc.ID No.:17873
Facility: Company-wide Revision 20
Department: Quality Assurance Published Date: 6/16/2023 4:52:28 PM
Title: Certificate/Approval Program Summary Page 1 of 1
Document Type: Form Pre-Qualtrax Document ID: 08-113
Certification Information
The following analytes are not included in our Primary NELAP Scope of Accreditation:
Westborough Facility
EPA 624.1: m/p-xylene, o-xylene, Naphthalene
EPA 625.1: alpha-Terpineol
EPA 8260D: NPW: 1,2,4,5-Tetramethylbenzene; 4-Ethyltoluene, Azobenzene; SCM: Iodomethane (methyl iodide), 1,2,4,5-Tetramethylbenzene; 4-
Ethyltoluene.
EPA 8270E: NPW: Dimethylnaphthalene,1,4-Diphenylhydrazine, alpha-Terpineol; SCM: Dimethylnaphthalene,1,4-Diphenylhydrazine.
SM4500: NPW: Amenable Cyanide; SCM: Total Phosphorus, TKN, NO2, NO3.
Mansfield Facility
SM 2540D: TSS.
EPA TO-15: Halothane, 2,4,4-Trimethyl-2-pentene, 2,4,4-Trimethyl-1-pentene, Thiophene, 2-Methylthiophene,
3-Methylthiophene, 2-Ethylthiophene, 1,2,3-Trimethylbenzene, Indan, Indene, 1,2,4,5-Tetramethylbenzene, Benzothiophene, 1-Methylnaphthalene.
Biological Tissue Matrix: EPA 3050B
The following analytes are included in our Massachusetts DEP Scope of Accreditation
Westborough Facility:
Drinking Water
EPA 300.0: Chloride, Nitrate-N, Fluoride, Sulfate; EPA 353.2: Nitrate-N, Nitrite-N; SM4500NO3-F: Nitrate-N, Nitrite-N; SM4500F-C, SM4500CN-CE,
EPA 180.1, SM2130B, SM4500Cl-D, SM2320B, SM2540C, SM4500H-B, SM4500NO2-B
EPA 524.2: THMs and VOCs; EPA 504.1: EDB, DBCP.
Microbiology: SM9215B; SM9223-P/A, SM9223B-Colilert-QT,SM9222D.
Non-Potable Water
SM4500H,B, EPA 120.1, SM2510B, SM2540C, SM2320B, SM4500CL-E, SM4500F-BC, SM4500NH3-BH: Ammonia-N and Kjeldahl-N, EPA 350.1:
Ammonia-N, LACHAT 10-107-06-1-B: Ammonia-N, EPA 351.1, SM4500NO3-F, EPA 353.2: Nitrate-N, SM4500P-E, SM4500P-B, E, SM4500SO4-E,
SM5220D, EPA 410.4, SM5210B, SM5310C, SM4500CL-D, EPA 1664, EPA 420.1, SM4500-CN-CE, SM2540D, EPA 300: Chloride, Sulfate, Nitrate.
EPA 624.1: Volatile Halocarbons & Aromatics,
EPA 608.3: Chlordane, Toxaphene, Aldrin, alpha-BHC, beta-BHC, gamma-BHC, delta-BHC, Dieldrin, DDD, DDE, DDT, Endosulfan I, Endosulfan II,
Endosulfan sulfate, Endrin, Endrin Aldehyde, Heptachlor, Heptachlor Epoxide, PCBs
EPA 625.1: SVOC (Acid/Base/Neutral Extractables).
Microbiology: SM9223B-Colilert-QT; Enterolert-QT, SM9221E, EPA 1600, EPA 1603, SM9222D.
Mansfield Facility:
Drinking Water
EPA 200.7: Al, Ba, Cd, Cr, Cu, Fe, Mn, Ni, Na, Ag, Ca, Zn. EPA 200.8: Al, Sb, As, Ba, Be, Cd, Cr, Cu, Pb, Mn, Ni, Se, Ag, TL, Zn. EPA 245.1 Hg.
EPA 522, EPA 537.1.
Non-Potable Water
EPA 200.7: Al, Sb, As, Be, Cd, Ca, Cr, Co, Cu, Fe, Pb, Mg, Mn, Mo, Ni, K, Se, Ag, Na, Sr, TL, Ti, V, Zn.
EPA 200.8: Al, Sb, As, Be, Cd, Cr, Cu, Fe, Pb, Mn, Ni, K, Se, Ag, Na, TL, Zn.
EPA 245.1 Hg.
SM2340B
For a complete listing of analytes and methods, please contact your Alpha Project Manager.
Serial_No:12112319:27
Page 15 of 16
Serial_No:12112319:27
Page 16 of 16
Massachusetts Department of Environmental Protection
eDEP Transaction Copy
Here is the file you requested for your records.
To retain a copy of this file you must save and/or print.
Username:
Transaction ID:
Document:
Size of File:
Status of Transaction:
Date and Time Created:
Note: This file only includes forms that were part of your
transaction as of the date and time indicated above. If you need
a more current copy of your transaction, return to eDEP and
select to “Download a Copy” from the Current Submittals page.
1641824
12/26/2023:12:38:47 PM
1079.95K
EBELAIR
Groundwater Discharge Monitoring Report Forms
Submitted
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
SERENITY BREWSTER WWTF
a. Name
873 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
MAHEEN AKHTER
a. Name of Facility Contact Person
6178526110 makhter@elevationfinancialgroup.com
b. Telephone Number c. email address
3. Sampling information:
11/2/2023 RI ANALYTICAL
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
KRISTIN PHELAN
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Discharge Monitoring Report 2023 Nov Monthly
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DISCHARGE MONITORING REPORT
599
1. Permit Number
475454704
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
D. Contaminant Analysis Information
For "0", below detection limit, less than (<) value, or not detected, enter "ND"
TNTC = too numerous to count. (Fecal results only)
NS = Not Sampled
1. Parameter/Contaminant 2. Influent 3. Effluent 4. Effluent Method
Units Detection limit
BOD 17 ND 3.0
MG/L
TSS 12 2.3 2.0
MG/L
TOTAL SOLIDS 260
MG/L
AMMONIAN 5.2
MG/L
NITRATEN 1.1 0.050
MG/L
TOTAL NITROGEN(NO3+NO2+TKN)2.7 0.50
MG/L
OIL & GREASE 0.80 0.50
MG/L
infeffrpblank.doc • rev. 09/15/15 Groundwater Permit Discharge Monitoring Report • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DISCHARGE MONITORING REPORT
599
1. Permit Number
475454704
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
SERENITY BREWSTER WWTF
a. Name
873 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
MAHEEN AKHTER
a. Name of Facility Contact Person
6178526110 makhter@elevationfinancialgroup.com
b. Telephone Number c. email address
3. Sampling information:
11/3/2023 WHITEWATER
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
RICK BRULOTTE
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Monitoring Well Data Report 2023 Nov Monthly
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
MONITORING WELL DATA REPORT
599
1. Permit Number
475454704
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
C. Contaminant Analysis Information
For "0", below detection limit, less than (<) value, or not detected, enter "ND"
TNTC = too numerous to count. (Fecal results only)
NS = Not Sampled
DRY = Not enough water in well to sample.
<
Parameter/Contaminant MW1 MW2 MW3 MW4
Units Well #: 1 Well #: 2 Well #: 3 Well #: 4 Well #: 5 Well #: 6
PH 6.4 6.9 6.9 7
S.U.
STATIC WATER LEVEL 59.4 58.1 59.5 29.25
FEET
SPECIFIC CONDUCTANCE 319 220 375 619
UMHOS/C
mwdgwpblank.doc • rev. 09/15/15 Monitoring Well Data for Groundwater Permit • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
MONITORING WELL DATA REPORT
599
1. Permit Number
475454704
2. Tax identification Number
2023 NOV MONTHLY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
A. Facility Information
1. Facility name, address:
SERENITY BREWSTER WWTF
a. Name
873 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
2. Contact information:
MAHEEN AKHTER
a. Name of Facility Contact Person
6178526110 makhter@elevationfinancialgroup.com
b. Telephone Number c. email address
3. Sampling information:
11/30/2023 WHITEWATER
a. Date Sampled (mm/dd/yyyy)b. Laboratory Name
RICK BRULOTTE
c. Analysis Performed By (Name)
B. Form Selection
1. Please select Form Type and Sampling Month & Frequency
Daily Log Sheet 2023 Nov Daily
All forms for submittal have been completed.
2.This is the last selection.
3.Delete the selected form.
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DAILY LOG SHEET
599
1. Permit Number
475454704
2. Tax identification Number
2023 NOV DAILY
3. Sampling Month & Frequency
C. Daily Readings/Analysis Information
Date Effluent
Flow GPD
Reuse
Flow GPD
Irrigation
Flow GPD
Turbidity Influent pH Effluent
pH
Chlorine
Residual
(mg/l)
UV
Intensity
(%)
1 8182 7.1
2 9135 7.1
3 7233 7 0.8
4 6672
5 7601
6 7280 6.9 0.8
7 8101 7.1 0.8
8 8637 6.5 0.6
9 6748 6.8 0.6
10 7320 7.2 0.2
11 6960
12 7705
13 6977 7 0.7
14 9452 7 1
15 7608 7 0.4
16 7415 6.9 0.6
17 7277 6.9 0.6
18 7639
19 6657
20 6270 7 0.9
21 8370 7 0.9
22 8838 7.1 0.8
23 7567
24 6971 7.2 0.6
25 7374
26 6850
27 8210 7.1 0.8
28 7601 7.2 0.8
29 8185 7.1 0.8
30 7512 7.1 0.8
31
gdpdls.doc • rev. 09/15/15 Groundwater Permit Daily Log Sheet • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
DAILY LOG SHEET
599
1. Permit Number
475454704
2. Tax identification Number
2023 NOV DAILY
3. Sampling Month & Frequency
Important:When
filling out forms on
the computer, use
only the tab key to
move your cursor
do not use the
return key.
Any person signing
a document under
314 CMR 5.14(1) or
(2) shall make the
following
certification
If you are filing
electronically and
want to attach
additional
comments, select
the check box.
Facility Information
SERENITY BREWSTER WWTF
a. Name
873 HARWICH ROAD
b. Street Address
BREWSTER MA 02631
c. City d. State e. Zip Code
Certification
“I certify under penalty of law that this document and all attachments were prepared under my direction or supervision in
accordance with a system designed to assure that qualified personnel properly gather and evaluate the information submitted.
Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate and complete. I am aware that there
are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations.”
ELIZABETH BELAIR 12/26/2023
a. Signature b. Date (mm/dd/yyyy)
Reporting Package Comments
FACILITY WAS IN FULL COMPLIANCE WITH ALL PERMIT REQUIREMENTS FOR THE MONTH
gdpdls 20150915.doc • rev. 09/15/15 Groundwater Permit • Page 1 of 1
Massachusetts Department of Environmental Protection
Bureau of Resource Protection Groundwater Discharge Program
Groundwater Permit
599
1. Permit Number
475454704
2. Tax identification Number
55 Walkers Brook Drive, Suite 100, Reading, MA 01867
Tel: 978.532.1900
Offices in: MA, CT, NH, VT, NY, NJ, PA, SC & FL
westonandsampson.com
November 22, 2023
Bryan Webb (via email)
Ocean Edge Resort
2907 Main Street
Brewster, MA 02631
RE: Ocean Edge Resort Wastewater Treatment Facility
Monthly Operations Report – October 2023
Dear Mr. Webb:
Enclosed please find the Monthly Operations Reporting Package for the Ocean Edge Resort wastewater treatment
facility (WWTF) located at 832 Village Drive in Brewster, MA.
Weston & Sampson Services, Inc. would like to note the following:
• All regulated effluent parameters of samples collected on October 23 were reported to be within their
respective permissible limits.
• Quarterly effluent samples were collected during this month.
• Quarterly monitoring well samples were collected during this month.
• Data was filed with MassDEP electronically, via eDEP. A copy of the transaction is included in this package.
If you have any questions or concerns regarding this report, or the wastewater treatment facility, please feel free
to contact me at wsscompliance@wseinc.com.
Regards,
WESTON & SAMPSON SERVICES, INC.
James R. Tringale
Compliance Coordinator
cc: Brewster Board of Health (via email)
FR Mahony Associates (via email)
Date Received:
Date Reported:
P.O. Number
Work Order #:
Project Name:
Enclosed are the analytical results and Chain of Custody for your project referenced above. The sample(s)
were analyzed by our Warwick, RI laboratory unless noted otherwise. When applicable subcontracted
results are noted and subcontracted reports are enclosed in their entirety.
All samples were analyzed within the established guidelines of US EPA approved methods with all
requirements met, unless otherwise noted at the end of a given sample's analytical results or in a case
narrative.
The Detection Limit is defined as the lowest concentration of an analyte that can be reliably detected under
routine laboratory conditions. The Reporting Limit is the minimum concentration that can be reliably
quantified under routine laboratory conditions .
These results only pertain to the samples submitted for this Work Order # and this report shall not be
reproduced except in its entirety.
We certify that the following results are true and accurate to the best of our knowledge . If you have
questions or need further assistance, please contact our Customer Service Department.
Approved by:
WSS Inc.dba Weston & Sampson
Christopher Vigneau
55 Walkers Brook Drive
Suite 100
Reading, MA 01867
10/24/2023
11/2/2023
2310-18143
PROJECT# 25364 OCEAN EDGE RESORT - QUARTERLY I+E
Attn:
Laboratory Certification Numbers (as applicable to sample's origin state):
Warwick RI * RI LAI00033, MA M-RI015, CT PH-0508
LABORATORY REPORT
Page 1 of 3
Katie Amaral, Ph.D., CMQ/OE
Laboratory Director
Report Qualifiers & Abbreviations
These qualifiers/abbreviations may or may not be present in this report.
Qualifier Descriptions
* Recovery outside of acceptance limits
B Analyte detected in method blank at a level about the detection limit
D Surrogate diluted out to reach a parameter result within the instrument calibration curve
E Parameter result exceeds calibration curve
J Estimated result based on MDL
Abbreviation Definition
BLK Method Blank
CFU Colony Forming Unit
DF Dilution Factor
DL Detection Limit
LCS(D) Laboratory Control Standard (Duplicate)
MCL Maximum Contaminant Level
MCLG Maximum Contaminant Level Goal
MDL Method Detection Limit
MPN Most Probable Number
MS(D) Matrix Spike (Duplicate)
QC Quality Control
RPD Relative Percent Difference
TIC Tentatively Identified Compound
TNTC Too Numerous to Count
*CS Field data provided by the client
Page 2 of 3
R.I. Analytical Laboratories, Inc.
Laboratory Report
Work Order #:
WSS Inc.dba Weston & Sampson
2310-18143
PROJECT# 25364 OCEAN EDGE RESORT - QUARTERLY I+EProject Name:
Page 3 of 3
PARAMETER RESULTS
SAMPLE
LIMIT
REP.
UNITS METHOD ANALYZED
DATE/TIME
ANALYST
Sample Type :
10/23/2023 @ 16:15
COMPOSITE
INFLUENT
001
Sample Date / Time :
Sample Description:
Sample Number:
BOD 5 HNB10/24/2023SM5210B 21edmg/L6063 19:11
Total Suspended Solids KPG10/26/2023SM2540D 2023mg/L2.0120 13:44
Total Solids BRC10/25/2023SM2540B 18-21edmg/L10530 19:57
Ammonia (as N)VC10/31/2023EPA 350.1mg/L0.407.6 11:10
PARAMETER RESULTS
SAMPLE
LIMIT
REP.
UNITS METHOD ANALYZED
DATE/TIME
ANALYST
Sample Type :
10/23/2023 @ 16:30
COMPOSITE
EFFLUENT
002
Sample Date / Time :
Sample Description:
Sample Number:
BOD 5 HNB10/24/2023SM5210B 21edmg/L10<10 19:11
Total Suspended Solids KPG10/26/2023SM2540D 2023mg/L2.012 13:44
Nitrite (as N)JW10/24/2023EPA 300.0mg/L0.050<0.050 20:34
Nitrate (as N)JW10/24/2023EPA 300.0mg/L0.050<0.050 20:34
TKN (as N)JCD10/30/2023SM4500NOrg-D 18-21edmg/L0.501.2 11:40
PARAMETER RESULTS
SAMPLE
LIMIT
REP.
UNITS METHOD ANALYZED
DATE/TIME
ANALYST
Sample Type :
10/23/2023 @ 16:45
GRAB
EFFLUENT
003
Sample Date / Time :
Sample Description:
Sample Number:
Orthophosphate JW10/25/2023SM4500 P E-2011mg/L0.0208.1 0:28
Total Phosphorus (as P)VC10/27/2023SM4500 P-B,E-2011mg/L0.0108.3 10:00
Oil & Grease Gravimetric ZAC11/1/2023EPA 1664Amg/L0.501.1 13:18
Orthophosphate - Filtered upon receipt at the laboratory. The filtration should occur
within fifteen minutes of sample collection.