Part 13 Waste Characterization and Figures Wayne Oakland DCSpec.pdf
PDF 2 MB Posted
- Attached to
- 761/20035. SAR Former Wayne Oakland Oil
- Solicitation number
- RFQ 171 200000000255 5
- Issued by
- Benzie County, Riverview City, Michigan
About this file
This document package contains a waste characterization laboratory report and bidding specification drawings for a remediation project involving the Michigan Department of Environment, Great Lakes, and Energy (EGLE)/Air Quality Division and the City of Royal Oak. The project involves the remediation of the Former Wayne Oakland Oil property located at 230 East Harrison Avenue in Royal Oak, Michigan. The work includes soil excavation and site restoration at an estimated depth of 10 to 14 feet, with excavation limits set at a 5-foot offset from perimeter fencing and existing block walls. The contractor is required to maintain stable side slopes of 1 horizontal to 1 vertical or shallower and must utilize the Miss Dig System to locate underground utilities at least 3 working days prior to commencing work. The project file number is 761-16136-SAR, with contract order number Y16184 and permanent ISD number 00592.
The analytical work was completed by Fibertec Environmental Services on October 11, 2019, with soil samples collected on July 24-25, 2019, analyzed in accordance with NELAC standards. Soil boring results from eleven locations (SB1 through SB11) identified contamination including benzene, naphthalene, 2-methylnaphthalene, and trimethylbenzene compounds exceeding Part 201 Generic Residential Cleanup Criteria in multiple samples. Groundwater sampling was performed at six boring locations with similar contaminants detected. The contractor must perform perimeter air monitoring using a photoionization detector (PID) and suppress site odors using odor-suppressing foam as necessary. Site restoration includes 6 inches of topsoil seeded and mulched, 4 inches of hot mix asphalt, and 4 inches of Portland cement concrete with 6x6 8/8 wire fabric, with all surfaces restored to match pre-construction conditions. Sample disposal protocols specify TO-15 samples will be disposed of 7 calendar days after reporting, while all other samples will be disposed of 30 days after the reporting date.
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Text version
Friday, October 11, 2019
230 Harrison Royal Oak, MI/Project Identification:
Fibertec Project Number: 92989
525 W. Allegan Street
Constitution Hall-3N
EGLE/AQD - Lansing District Office
Lansing, MI 48909
Ms. Kim Ethridge
Thank you for selecting Fibertec Environmental Services as your analytical laboratory. The samples you submitted have been analyzed in accordance with NELAC standards and the results compiled in the attached report. Any exceptions to NELAC compliance are noted in the report. These results apply only to those samples submitted. Please note TO-15 samples will be disposed of 7 calendar days after the reporting date. All other samples will be disposed of 30 days after the reporting date.
Dear Ms. Ethridge, Submittal Date: 10/03/2019
If you have any questions regarding these results or if we may be of further assistance to you, please contact me at (517) 699-0345.
Sincerely, For Daryl P. Strandbergh Laboratory Director
Enclosures
In regards to this project, 230 Harrison (M100), the file number is 761-16136-SAR. The contract order number is Y16184.
Our permanent ISD number is 00592. The Activity Code is M100.
By Stephannie Wallace at 3:27 PM, Oct 11, 2019
1914 Holloway Drive Holt, MI 48842 T: (517) 699-0345
11766 E. Grand River Brighton, MI 48116 T: (810) 220-3300
8660 S. Mackinaw Trail Cadillac, MI 49601 T: (231) 775-8368 lab@fibertec.us
F: (517) 699-0388
F: (810) 220-3311
F: (231) 775-8584
DCSID: G-610.19 (10/01/19) RSN: 92989-191011152635
Laboratory Sample Number: 92989-001
Analytical Laboratory Report 92989
Order:
Page:
Date: 10/11/19
Client Identification: EGLE/AQD - Lansing District Office
Client Project Name: 230 Harrison
Client Project No: NA
Sample Description: TCLP1
Sample No: 1
Sample Matrix: Soil/Solid
Collect Date:
Chain of Custody: 180972
Collect Time: 09:30
Laboratory Project Number: 92989
Sample Comments: Soil results have been calculated and reported on a dry weight basis unless otherwise noted.
Q: Qualifier (see definitions at end of report) NA: Not ApplicableDefinitions:
10/02/19
: Parameter not included in NELAC Scope of Analysis.‡
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: Toxicity Characteristic Leaching Procedure (TCLP) Soil/SolidMatrix:92989-001
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 1311
NA1. 10/7/2019 NA 1.0 NA NA 10/07/19 NATCLP Date CMB
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: Toxicity Characteristic Leaching Procedure (TCLP), Zero Headspace Soil/SolidMatrix:92989-001
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 1311
NA1. 10/7/2019 NA 1.0 NA NA 10/07/19 NATCLP Date CM
1914 Holloway Drive Holt, MI 48842 T: (517) 699-0345
11766 E. Grand River Brighton, MI 48116 T: (810) 220-3300
8660 S. Mackinaw Trail Cadillac, MI 49601 T: (231) 775-8368 lab@fibertec.us
F: (517) 699-0388
F: (810) 220-3311
Order:
Page:
Date: 10/11/19
Client Identification: EGLE/AQD - Lansing District Office
Client Project Name: 230 Harrison
Client Project No: NA
Sample Description: TCLP1
Sample No: 1
Sample Matrix: Soil/Solid
Collect Date:
Chain of Custody: 180972
Collect Time: 09:30
Laboratory Project Number: 92989
Sample Comments: Soil results have been calculated and reported on a dry weight basis unless otherwise noted.
Q: Qualifier (see definitions at end of report) NA: Not ApplicableDefinitions:
10/02/19
: Parameter not included in NELAC Scope of Analysis.‡
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: TCLP RCRA-8 Metals by ICP-MS TCLP ExtractMatrix:92989-001B
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 3005A (Total Recoverable)/EPA 6020A mg/L1. U 1.0 20 10/08/19 PT19J08D 10/09/19 T419J09AArsenic JLH mg/L2. U 1.0 20 10/08/19 PT19J08D 10/09/19 T419J09ABarium JLH mg/L3. U 0.20 20 10/08/19 PT19J08D 10/09/19 T419J09ACadmium JLH mg/L4. U 1.0 20 10/08/19 PT19J08D 10/09/19 T419J09AChromium JLH mg/L5. U 1.0 20 10/08/19 PT19J08D 10/09/19 T419J09ALead JLH mg/L6. U 0.20 20 10/08/19 PT19J08D 10/09/19 T419J09ASelenium JLH mg/L7. U 1.0 20 10/08/19 PT19J08D 10/09/19 T419J09ASilver JLH
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: TCLP Mercury TCLP ExtractMatrix:92989-001B
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 7470A mg/L1. U 0.050 8.0 10/11/19 PM19J11B 10/11/19 M719J11AMercury CJA
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: TCLP Volatiles TCLP ExtractMatrix:92989-001C
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 5030C/EPA 8260D mg/L1. U 0.10 200 10/08/19 VB19J08B 10/08/19 VB19J08BBenzene ZJJ mg/L2. U 40 200 10/08/19 VB19J08B 10/08/19 VB19J08B2-Butanone ZJJ mg/L3. U 0.10 200 10/08/19 VB19J08B 10/08/19 VB19J08BCarbon Tetrachloride ZJJ mg/L4. U 20 200 10/08/19 VB19J08B 10/08/19 VB19J08BChlorobenzene ZJJ mg/L5. U 1.2 200 10/08/19 VB19J08B 10/08/19 VB19J08BChloroform ZJJ mg/L6. U 1.5 200 10/08/19 VB19J08B 10/08/19 VB19J08B1,4-Dichlorobenzene ZJJ mg/L7. U 0.10 200 10/08/19 VB19J08B 10/08/19 VB19J08B1,2-Dichloroethane ZJJ
F+ mg/L8. U 0.14 200 10/08/19 VB19J08B 10/08/19 VB19J08B1,1-Dichloroethene ZJJ mg/L9. U 0.14 200 10/08/19 VB19J08B 10/08/19 VB19J08BTetrachloroethene ZJJ mg/L10. U 0.10 200 10/08/19 VB19J08B 10/08/19 VB19J08BTrichloroethene ZJJ mg/L11. U 0.20 200 10/08/19 VB19J08B 10/08/19 VB19J08BVinyl Chloride ZJJ
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: TCLP Semivolatiles TCLP ExtractMatrix:92989-001A
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 3510C/EPA 8270E
G+ mg/L1. U 0.025 1.4 10/08/19 PS19J08D 10/08/19 SN19J08B2,4-Dinitrotoluene GJP
1914 Holloway Drive Holt, MI 48842 T: (517) 699-0345
11766 E. Grand River Brighton, MI 48116 T: (810) 220-3300
8660 S. Mackinaw Trail Cadillac, MI 49601 T: (231) 775-8368 lab@fibertec.us
F: (517) 699-0388
F: (810) 220-3311
Order:
Page:
Date: 10/11/19
Client Identification: EGLE/AQD - Lansing District Office
Client Project Name: 230 Harrison
Client Project No: NA
Sample Description: TCLP1
Sample No: 1
Sample Matrix: Soil/Solid
Collect Date:
Chain of Custody: 180972
Collect Time: 09:30
Laboratory Project Number: 92989
Sample Comments: Soil results have been calculated and reported on a dry weight basis unless otherwise noted.
Q: Qualifier (see definitions at end of report) NA: Not ApplicableDefinitions:
10/02/19
: Parameter not included in NELAC Scope of Analysis.‡
Analysis
Reporting Limit Parameter(s) Result
Preparation
UnitsQ Dilution
Aliquot ID: TCLP Semivolatiles TCLP ExtractMatrix:92989-001A
P. Date P. Batch A. Date A. Batch Init.
Description: TCLP1Method: EPA 3510C/EPA 8270E
G+ mg/L2. U 0.025 1.4 10/08/19 PS19J08D 10/08/19 SN19J08BHexachlorobenzene GJP
G+ mg/L3. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08BHexachlorobutadiene GJP
L- mg/L4. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08BHexachloroethane GJP
G+ mg/L5. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08B2-Methylphenol GJP
G+ mg/L6. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08B3&4-Methylphenol‡ GJP
G+ mg/L7. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08BNitrobenzene GJP
G+ mg/L8. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08BPentachlorophenol GJP
G+ mg/L9. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08BPyridine GJP
G+ mg/L10. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08B2,4,5-Trichlorophenol GJP
G+ mg/L11. U 0.10 1.4 10/08/19 PS19J08D 10/08/19 SN19J08B2,4,6-Trichlorophenol GJP
1914 Holloway Drive Holt, MI 48842 T: (517) 699-0345
11766 E. Grand River Brighton, MI 48116 T: (810) 220-3300
8660 S. Mackinaw Trail Cadillac, MI 49601 T: (231) 775-8368 lab@fibertec.us
F: (517) 699-0388
F: (810) 220-3311
Spike recovery or precision unusable due to dilution.
Definitions/ Qualifiers:
The analyte was detected in the associated method blank.
The analyte was detected at a concentration greater than the calibration range, therefore the result is estimated.
The concentration is an estimated value.
The analyte was not detected at or above the reporting limit.
Matrix Interference has resulted in a raised reporting limit or distorted result.
Results reported on a wet-weight basis.
Value reported is outside QC limits
A:
B:
E:
J:
U:
X:
W:
Analytical Laboratory Report 92989
Order:
Page:
Date: 10/11/19 Laboratory Project Number: 92989
Exception Summary:
Modified MethodM:
Analysis Locations:
All analyses performed in Holt.
Recovery from the spiked aliquot exceeds the upper control limit (matrix spike or matrix spike duplicate).F+ :
Recovery of the associated Surrogate Compound exceeds the upper control limit. Results may be biased high.G+ :
Recovery in the associated laboratory sample (LCS) exceeds the lower control limit. Results may be biased low.L- :
T104704518-19-8 (TX)
Accreditation Number(s):
1914 Holloway Drive Holt, MI 48842 T: (517) 699-0345
11766 E. Grand River Brighton, MI 48116 T: (810) 220-3300
8660 S. Mackinaw Trail Cadillac, MI 49601 T: (231) 775-8368 lab@fibertec.us
F: (517) 699-0388
F: (810) 220-3311
Bidding and Contract Document (R 11/19) Project Name: Former Wayne Oakland Oil File No. 761/20035.SAR
DRAWINGS
EAST HARRISON AVENUE
D E
L A
W A
R E
A
V E
N U
E
Project
Project Location
Sheet Name
CADD
Scale
Project
No.
Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e v b i d s p e c s
C
O V
E R d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L
O T
T
E
M a r a m p l a c e www.sme-usa.com
FORMER WAYNE
OAKLAND OIL
REMEDIATION
230 EAST HARRISON
AVENUE
ROYAL OAK,
MICHIGAN
PROPERTY LOCATION
COVER SHEET
3-4-2020
JAB
CTV
AS NOTED
083103.00
LOCATION MAP
SCALE: 1" = 60'
AREA
OF WORK
FORMER WAYNE OAKLAND OIL REMEDIATION
ROYAL OAK, MICHIGAN
LIST OF DRAWINGS
FIGURE No. SHEET TITLE
COUNTY MAP
NOT TO SCALE
Know what'sbelow.
before you dig.Call
OAKLAND
COUNTY
1. Property Location Cover Sheet
2. Former and Existing Site Features
3. Soil Boring Soil Sample Analytical Results
4. Soil Boring Groundwater Sample Analytical Results
5. Excavation Plan
6. Stratigraphic Cross Sections
7. Site Restoration Plan
X
X
X
X
X
X
X
X
X
X
X
X
X
X
OH
OH
G A
S
O
H
O
H
O
H
O
H
D
D
D
D
D
D
D
D
D
D
D
D
GRASS
GRASS
ASPHALT
PARKING
LOT
X
X
X
X
X
X
X
X
X
EXISTING HANDICAP SIGN
EXISTING PAVEMENT
MARKINGS
Project
Project Location
Sheet Name www.sme-usa.com
CADD
Scale
Project
No.
Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e e c s
S
I T
E d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L
T
E
M a r a m p l a c e
FORMER WAYNE
OAKLAND OIL
REMEDIATION
230 EAST HARRISON
AVENUE, ROYAL OAK,
MICHIGAN
FORMER AND
EXISTING SITE
FEATURES
3/4/2020
CRP
CRP
1" = 30'
083103.00
LEGEND
PROPERTY BOUNDARY
NOTES:
1. FORMER SITE FEATURES OBTAINED FROM MALCOLM AND PIRNIE DRAWING TITLED "HISTORIC SITE FEATURES" FIGURE 3, DATED MARCH 2012. EXISTING SITE FEATURES OBTAINED FROM GOOGLE EARTH PRO IMAGERY DATED 4/23/2019 AND SITE
RECONNAISSANCE.
2. AST - ABOVE GROUND STORAGE TANK, UST - UNDERGROUND STORAGE TANK.
3. USTs/ASTs SHOWN ON THIS DRAWING HAVE REPORTEDLY BEEN REMOVED.
4. ALL UTILITY LOCATIONS ARE APPROXIMATE AND WERE OBTAINED FROM MISS DIG DESIGN TICKET #B93100573 AND
MALCOLM AND PIRNIE DRAWING TITLED "SITE BASE MAP" FIGURE 2, DATED MARCH 2012.
EAST HARRISON AVENUE
D E
L A
W A
E
N U
E
GAMER SALOON
230 E. HARRISON
METRO LOFTS
322 E. HARRISON
STATION 3 LOFTS
333 E. PARENT
PROPERTY BOUNDARY
EXISTING BLOCK WALL
XX
EXISTING CHAIN-LINK FENCE
XX
EXISTING CHAIN-LINK TO BE REMOVED
AND RE-INSTALLED
XX
TEMPORARY 6 FT. TALL CHAIN-LINK
SECURITY FENCE
WATER MAIN
STORM SEWER
SANITARY SEWER
GAS
GAS MAIN
EXISTING STRUCTURES
PAVEMENT EDGE
PORTLAND CEMENT CONCRETE
FORMER SITE FEATURES LEGEND
1- 9
20,000 GALLON FUEL OIL AST
10 REMEDIATION SYSTEM
11 CLAY DIKE
12- 13 UST EXCAVATION
3,000 GALLON UST
15 PUMPS
16 LOADING PAD
17 CONCRETE DIKE
18 DIESEL PUMP ISLAND
1,100 GALLON DIESEL AST
20,000 GALLON UNLEADED GAS AST
21-22
16,600 FUEL OIL AST
23-24
16,600 UNLEADED/LEADED GAS AST
25-26
AST (CONTENTS AND SIZE UNKNOWN)
0'
GRAPHIC SCALE: 1" = 30'
30' 60'
UNKNOWN GPR ANOMALY (POTENTIAL UTILITY)
D
MANHOLE/CATCH BASIN/DRAIN
UTILITY POLE
BURIED CABLE
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
SB6
SB1
SB2
SB3
SB4
SB5
SB7
SB8
SB9
SB10
SB11
Project
Project Location
Sheet Name www.sme-usa.com
CADD
Scale
Project
No.
Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e e c s s o i l a n a l y t i c a l d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L
T
E
M a r a m p l a c e
FORMER WAYNE
OAKLAND OIL
REMEDIATION
230 EAST HARRISON
AVENUE, ROYAL OAK,
MICHIGAN
SOIL BORING
SOIL SAMPLE
ANALYTICAL
RESULTS
3/4/2020
CRP
CRP
1" = 30'
083103.00
LEGEND
SITE PROPERTY BOUNDARY
NOTES:
1. CONCENTRATIONS REPORTED IN (µg/kg) AND EXCEED ONE OR MORE PART 201 GENERIC RESIDENTIAL CLEANUP CRITERIA.
2. NAPHTHALENE CONCENTRATIONS SHOWN ARE THE HIGHER OF THE VOLATILE AND SEMI-VOLATILE CONCENTRATIONS.
3. SOIL BORINGS WERE PERFORMED IN JULY 2019.
4. EXISTING SITE FEATURES OBTAINED FROM GOOGLE EARTH PRO IMAGERY DATED 4/23/2019 AND SITE RECONNAISSANCE.
ADJACENT PROPERTY BOUNDARY
EXISTING BLOCK WALL
XX
EXISTING CHAIN-LINK FENCE
XX
EXISTING CHAIN-LINK TO BE REMOVED
AND RE-INSTALLED
XX
TEMPORARY 6 FT. TALL CHAIN-LINK
SECURITY FENCE
EXISTING STRUCTURES
PAVEMENT EDGE
PORTLAND CEMENT CONCRETE
0'
GRAPHIC SCALE: 1" = 30'
30' 60'
EXCAVATION LIMITS
ESTIMATED DEPTH: 10 FT -14 FT
D E
L A
W A
E
N U
E
GAMER SALOON
230 E. HARRISON
SB9 (4.5' - 5.5')
7/25/2019
Dibenzofuran 3,400
1,2,4-Trimethylbenzene 44,000
2-Methylnaphthalene 83,000
Ethylbenzene 7,500
Naphthalene 24,000 n-Butylbenzene 6,000 n-Propylbenzene 4,900 sec-Butylbenzene 2,500
Phenanthrene 6,000
EAST HARRISON AVENUE
SB8-SAT (8.0'-9.0')
7/24/2019
1,2,4-Trimethylbenzene 1,500
Isopropylbenzene 5,000 n-Butylbenzene 11,000 n-Propylbenzene 19,000 sec-Butylbenzene 5,900
SB7-SAT (7.8'-8.5')
7/24/2019 n-Butylbenzene 2,600 n-Propylbenzene 2,400
SB6-SAT (8.0'-9.0')
7/24/2019
Phenanthrene 5,700
1,2,4-Trimethylbenzene 44,000
1,3,5-Trimethylbenzene 6,700
Isopropylbenzene 6,600 n-Butylbenzene 22,000 n-Propylbenzene 14,000 sec-Butylbenzene 10,000
SB5-SAT (8.0'-9.0')
7/24/2019
Phenanthrene 3,500
1,2,4-Trimethylbenzene 26,000
2-Methylnaphthalene 120,000
Isopropylbenzene 6,900
Naphthalene 17,000 n-Butylbenzene 19,000 n-Propylbenzene 14,000 sec-Butylbenzene 11,000
SB4 (6.0'-7.0')
7/24/2019
1,2,4-Trimethylbenzene 120,000
1,3,5-Trimethylbenzene 3,300
2-Methylnaphthalene 300,000
Ethylbenzene 22,000
Isopropylbenzene 8,800
Naphthalene 96,000 n-Butylbenzene 24,000 n-Propylbenzene 21,000
Phenanthrene 18,000 sec-Butylbenzene 12,000
SB3-SAT (8.0'-9.0')
7/24/2019
Phenanthrene 3,400
1,2,4-Trimethylbenzene 39,000
2-Methylnaphthalene 76,000
Ethylbenzene 5,900
Naphthalene 26,000 n-Butylbenzene 7,700 n-Propylbenzene 6,600 sec-Butylbenzene 3,900
SB2 (6.0'-7.0')
7/24/2019
1,2,4-Trimethylbenzene 74,000
1,3,5-Trimethylbenzene 26,000
2-Methylnaphthalene 170,000
Acenaphthene 10,000
Dibenzofuran 11,000
Ethylbenzene 8,900
Fluorene 16,000
Isopropylbenzene 4,100
Naphthalene 63,000 n-Propylbenzene 9,900
Phenanthrene 33,000 sec-Butylbenzene 8,400
SB1 (8.0'-9.0')
7/24/2019
1,2,4-Trimethylbenzene 9,200
1,3,5-Trimethylbenzene 1,400 n-Butylbenzene 6,000 n-Propylbenzene 4,100 sec-Butylbenzene 3,600
SB9
SOIL BORING LOCATION WITH CHEMICAL
CONSTITUENTS IN SOIL ABOVE PART 201
GENERIC RESIDENTIAL CLEANUP CRITERIA
SB10
SOIL BORING LOCATION WITH CHEMICAL
CONSTITUENTS IN SOIL BELOW PART 201
GENERIC RESIDENTIAL CLEANUP CRITERIA
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
SB6
SB1
SB2
SB3
SB4
SB5
SB7
SB8
SB9
SB10
SB11
Project
Project Location
Sheet Name www.sme-usa.com
CADD
Scale
Project
No.
Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e e c s g w a n a l y t i c a l d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L
T
E
M a r a m p l a c e
FORMER WAYNE
OAKLAND OIL
REMEDIATION
230 EAST HARRISON
AVENUE, ROYAL OAK,
MICHIGAN
SOIL BORING
GROUNDWATER
SAMPLE
ANALYTICAL
RESULTS
3/4/2020
CRP
CRP
1" = 30'
083103.00
LEGEND
SITE PROPERTY BOUNDARY
NOTES:
1. CONCENTRATIONS REPORTED IN (µg/kg) AND EXCEED ONE OR MORE PART 201 GENERIC RESIDENTIAL CLEANUP CRITERIA.
2. NAPHTHALENE CONCENTRATIONS SHOWN ARE THE HIGHER OF THE VOLATILE AND SEMI-VOLATILE CONCENTRATIONS.
3. SOIL BORINGS WERE PERFORMED IN JULY 2019.
4. EXISTING SITE FEATURES OBTAINED FROM GOOGLE EARTH PRO IMAGERY DATED 4/23/2019 AND SITE RECONNAISSANCE.
ADJACENT PROPERTY BOUNDARY
EXISTING BLOCK WALL
XX
EXISTING CHAIN-LINK FENCE
XX
EXISTING CHAIN-LINK TO BE REMOVED
AND RE-INSTALLED
XX
TEMPORARY 6 FT. TALL CHAIN-LINK
SECURITY FENCE
EXISTING STRUCTURES
PAVEMENT EDGE
PORTLAND CEMENT CONCRETE
0'
GRAPHIC SCALE: 1" = 30'
30' 60'
EXCAVATION LIMITS
ESTIMATED DEPTH: 10 FT- 14 FT
GAMER SALOON
230 E. HARRISON
SB9 (6.0' - 10.0')
7/25/2019
1,2,4-Trimethylbenzene 19
2-Methylnaphthalene 400
Benzene 6.1
Ethylbenzene 37
Naphthalene 330
Phenanthrene 28
EAST HARRISON AVENUE
SB5 (10.0'-14.0')
7/24/2019
1,2,4-Trimethylbenzene 62
2-Methylnaphthalene 240
Benzene 7.9
Fluorene 15
Naphthalene 110
Phenanthrene 31
SB4 (7.0'-11.0')
7/24/2019
1,2,4-Trimethylbenzene 56
2-Methylnaphthalene 87
Benzene 5.0
Ethylbenzene 20
Naphthalene 56
SB2 (7.0'-11.0')
7/24/2019
1,2,4-Trimethylbenzene 100
2-Methylnaphthalene 160
Benzene 160
Ethylenzene 28
Naphthalene 91
Phenanthrene 3.3
SB1 (8.0'-12.0')
7/24/2019
1,2,4-Trimethylbenzene 100
Dibenzofuran 6.5
Phenanthrene 9.0
SB9
SOIL BORING LOCATION WITH CHEMICAL
CONSTITUENTS IN GROUNDWATER
ABOVE PART 201 GENERIC RESIDENTIAL
CLEANUP CRITERIA
SB10
SOIL BORING LOCATION WHERE
GROUNDWATER WAS NOT SAMPLED
D E
L A
W A
E
N U
SB10 SB9 SB5 SB6 SB7
A A'
E L E
V A
T I O
N
I N
F
E T
E L E
V A
T I O
N
E T
LEAN CLAY
LEAN CLAY
FINE SAND
TOPSOIL
TOPSOIL
PROPERTY
BOUNDARY
SANDY
GRAVEL
FINE SAND
SAND FILL
SAND FILL
CONCRETE
ASPHALT
SB5SB8 SB3 SB2
B B'
E L E
V A
T I O
N
E T
E L E
V A
T I O
N
E T
PROPERTY
BOUNDARY
TOPSOIL
PROPERTY
BOUNDARY
SAND FILL
SAND FILL
FINE SAND
FINE SAND
LEAN CLAY
LEAN CLAY
SB1
SB4
SB11
A
A'
B
B'
SB9
SB6
SB2
SB3SB5
SB7
SB8
SB10
Project
Project Location
Sheet Name www.sme-usa.com
CADD
Scale
Project
No. Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e e c s
X
S E
C T
I O
N S d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L O
T
D
A T
E
F I L
L
C A
T I O
N
M a r a m p l a c e
FORMER WAYNE
OAKLAND OIL
REMEDIATION
230 EAST HARRISON
AVENUE
ROYAL OAK,
MICHIGAN
STRATIGRAPHIC
CROSS SECTIONS
3/6/20
JAB/CRP
CTV/CRP
AS SHOWN
083103.00
ASPHALT
SAND FILL
LEGEND
CONCRETE
FINE SAND
SANDY GRAVEL
LEAN CLAY
STAINING AND ODORS
WATER TABLE
ELEVATION
APPROXIMATE
EXCAVATION
LIMITS
CROSS SECTION A-A'
CROSS SECTION B-B'
VERTICAL SCALE: 1" = 6'
HORIZONTAL SCALE: 1" = 30'
LOCATION MAP
SCALE: 1" = 80'
NOTES:
1. SOIL STRATUM TYPE AND ELEVATIONS AREA INFERRED
BETWEEN SOIL BORING LOCATIONS AND MAY VARY.
2. WATER TABLE ELEVATION INFERRED FROM SME JULY 2019 SOIL
BORINGS.
3. EXCAVATION LIMITS ARE AT A 5 FOOT OFFSET FROM PERIMETER
FENCING AND EXISTING BLOCK WALL. CONTRACTOR SHALL
MAINTAIN AN EXCAVATION SIDE SLOPE OF 1H:1V OR
SHALLOWER AS CONDITIONS WARRANT TO MAINTAIN A STABLE
SIDEWALL.
VERTICAL SCALE: 1" = 6'
HORIZONTAL SCALE: 1" = 30'
TOPSOIL
X
X
X
X
X
X
X
X
X
X
X
X
X
OH
OH
O
H
O
H
D
D
D
D
D
D
D
D
D
D
X
X
X
X
X
X
X
X
X
SB1
SB2
SB3
SB4
SB5
SB6
SB7
SB8
SB9
SB10
SB11
BM
Project
Project Location
Sheet Name www.sme-usa.com
CADD
Scale
Project
No.
Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e e c s
E
X C
A V d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L
T
E
M a r a m p l a c e
FORMER WAYNE
OAKLAND OIL
REDMEDIATION
230 EAST HARRISON
AVENUE, ROYAL OAK,
MICHIGAN
EXCAVATION PLAN
3/6/20
CRP/JAB
CRP
AS SHOWN
083103.00
LEGEND
SITE PROPERTY BOUNDARY
ESTIMATED DEPTH: 10 FT - 14 FT
EAST HARRISON AVENUE
D E
L A
W A
E
N U
E
GAMER SALOON
230 E. HARRISON
METRO LOFTS
322 E. HARRISON
STATION 3 LOFTS
333 E. PARENT
ADJACENT PROPERTY BOUNDARY
EXISTING BLOCK WALL
XX
EXISTING CHAIN LINK FENCE
XX
EXISTING CHAIN LINK TO BE REMOVED
AND RE-INSTALLED
XX
TEMPORARY 6 FT. TALL CHAIN LINK
SECURITY FENCE
WATER MAIN
STORM SEWER
SANITARY SEWER
GAS
GAS MAIN
EXISTING STRUCTURES
PAVEMENT EDGE
PORTLAND CEMENT CONCRETE
0'
GRAPHIC SCALE: 1" = 30'
30' 60'
UNKNOWN GPR ANOMALY (POTENTIAL UTILITY)
EXCAVATION LIMITS
D
MANHOLE/CATCH BASIN/DRAIN
UTILITY POLE
BURIED CABLE
APPROXIMATE SOIL BORING LOCATION
EXCAVATION BOTTOM (ESTIMATED DEPTH = 10'-14')
SLOPE, 1H:1V
OR SHALLOWER AS CONDITIONS WARRANT
NOTES:
1. CONTRACTOR SHALL TAKE PROPER PRECAUTIONS TO PROTECT ABOVE AND BELOW GROUND UTILITIES , EXISTING SIDEWALKS, EXISTING SITE FEATURES, AND ADJACENT PROPERTY AND STRUCTURES.
2. THE CONTRACTOR SHALL UTILIZE THE MISS DIG SYSTEM TO LOCATE ALL UNDERGROUND UTILITIES AT LEAST 3 WORKING DAYS PRIOR TO COMMENCEMENT OF WORK.
3. SAWCUT CONCRETE AND HMA PAVEMENTS AT THE LOCATIONS SHOWN ON THE DRAWINGS.
4. EXCAVATION LIMITS ARE AT A 5 FEET OFFSET FROM PERIMETER FENCING AND EXISTING BLOCK WALL. CONTRACTOR SHALL MAINTAIN AN EXCAVATION SIDE SLOPE OF 1 VERTICAL TO 1 HORIZONTAL OR SHALLOWER AS CONDITIONS WARRANT TO
MAINTAIN A STABLE SIDE SLOPE. PRIOR TO ANY PERSONS ENTERING THE EXCAVATION AND AT THE END OF EACH DAY THE SIDE WALLS OF THE EXCAVATION SHOULD BE BACKFILLED TO 1 VERTICAL TO 2 HORIZONTAL SLOPE.
5. THE CONTRACTOR SHALL CONTACT THE OWNER OF ANY UTILITIES ENCOUNTERED DURING EXCAVATION TO DETERMINE COURSE OF ACTION. INACTIVE UTILITIES WITH UNKNOWN OWNER SHALL BE CUT AND CAPPED AT THE EXCAVATION LIMITS.
6. THE PROFESSIONAL SHALL PERFORM PERIMETER AIR MONITORING UTILIZING A PHOTOIONIZATION DECTECTOR (PID) TO SCREEN AMBIENT AIR FOR VOLATILE ORGANIC COMPOUNDS (VOCs). THE CONTRACTOR SHALL SUPPRESS SITE ODORS USING
ODOR SUPPRESSING FOAM AS DEEMED NECESSARY BY THE PROFESSIONAL.
7. THE EXISTING HANDICAP SIGN AND NORTHERN PERIMETER FENCE SHOWN ABOVE, SHALL BE REMOVED AND STORED UNDAMAGED FOR RE-INSTALLATION DURING SITE RESTORATION.
8. ALL UTILITY LOCATIONS ARE APPROXIMATE AND WERE OBTAINED FROM MISS DIG DESIGN TICKET #B93100573 AND MALCOLM AND PIRNIE DRAWING TITLED "SITE BASE MAP" FIGURE 2, DATED MARCH 2012.
9. EXISTING SITE FEATURES OBTAINED FROM GOOGLE EARTH PRO IMAGERY DATED 4/23/2019 AND SITE RECONNAISSANCE.
EXISTING HANDICAP SIGN
SAWCUT PAVEMENT
BM
BENCHMARK AT SE PATIO DOOR AT GROUND
SURFACE (ASSUMED ELEVATION = 100.0 FT)
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
Project
Project Location
Sheet Name www.sme-usa.com
CADD
Scale
Project
No.
Revision Date
Designer
Date
S m e i n c p z W
I P
C
A D
D
W G
S E n v r e e c s r e s t d w g
NO REPRODUCTION SHALL BE MADE WITHOUT THE PRIOR
CONSENT OF SME
c
DRAWING NOTE: SCALE DEPICTED IS MEANT FOR 11" X 17"
AND WILL SCALE INCORRECTLY IF PRINTED ON ANY
OTHER SIZE MEDIA
Figure No.
P L
T
E
M a r a m p l a c e
FORMER WAYNE
OAKLAND OIL
REMEDIATION
230 EAST HARRISON
AVENUE, ROYAL OAK,
MICHIGAN
SITE RESTORATION
3/6/20
CRP
CRP
1" = 30'
083103.00
LEGEND
SITE PROPERTY BOUNDARY
NOTES:
1. SURFACES SHOULD BE GRADED TO MATCH PRE-CONSTRUCTION CONDITIONS.
2. ANY DAMAGE OR DISTURBANCE TO PUBLIC AND/OR ADJACENT PARCELS SHALL BE REPAIRED TO PRE-CONSTRUCTION
CONDITIONS AT THE SOLE EXPENSE OF THE CONTRACTOR.
3. EXISTING SITE FEATURES OBTAINED FROM GOOGLE EARTH PRO IMAGERY DATED 4/23/2019 AND SITE RECONNAISSANCE.
ADJACENT PROPERTY BOUNDARY
EXISTING BLOCK WALL
XX
EXISTING CHAIN LINK FENCE
XX
EXISTING CHAIN LINK TO BE REMOVED
AND RE-INSTALLED
XX
TEMPORARY 6 FT. TALL CHAIN LINK
SECURITY FENCE
EXISTING STRUCTURES
PAVEMENT EDGE
PORTLAND CEMENT CONCRETE
0'
GRAPHIC SCALE: 1" = 30'
30' 60'
GAMER SALOON
230 E. HARRISON
EAST HARRISON AVENUE
D E
L A
W A
E
N U
E
6" OF TOPSOIL - SEEDED AND MULCHED
4" OF HOT MIX ASPHALT
4" OF PORTLAND CEMENT CONCRETE
WITH 6X6 8/8 WWF
PAVEMENT MARKINGS TO MATCH
PRE-CONSTRUCTION CONDITIONS
RE-INSTALL HANDICAP SIGN
RE-INSTALL CHAIN-LINK FENCE
NOT TO SCALE
TYPICAL BACKFILL CROSS-SECTION
NOT TO SCALE
HMA PAVEMENT CROSS-SECTION
NOTE: APPLY TACK COAT OF SS-IH (0.05 GALLONS/S.Y.) BETWEEN ALL HMA LAYERS, VERTICAL CONCRETE AND HMA SURFACES, AND ALL EMBEDMENTS. ALL SURFACE SHALL BE FREE OF DIRT AND DEBRIS PRIOR TO PLACEMENT OF TACK AND HMA.
2'
MDOT CLASS II SAND COMPACTED TO 95% OF MAXIMUM
DRY DENSITY AS DETERMINED BY THE MODIFIED PROCTOR
TEST.
EXCAVATION SIDEWALL
EXCAVATION SIDEWALL
MIN. 2" MDOT 36A COMPACTED OVER MIN.
2" MDOT 13A COMPACTED TO 92% TO 96%
OF THE THEORETICAL MAX. DENSITY (TMD)
AS DETERMINED BY THE JOB MIX FORMULA
(JMF)
8 INCHES OF MDOT 21AA CRUSHED
LIMESTONE COMPACTED TO 95% OF
MAXIMUM DRY DENSITY AS DETERMINED BY
THE MODIFIED PROCTOR TEST
2'
6 INCHES OF TOPSOIL - SEEDED AND
MULCHED
PORTLAND CEMENT CONCRETE CROSS-SECTION
EXCAVATION SIDEWALL
MDOT CLASS II SAND COMPACTED TO 95%
OF MAXIMUM DRY DENSITY AS DETERMINED
BY THE MODIFIED PROCTOR TEST.
MIN. 4" 4000 PSI PORTLAND CEMENT
CONCRETE AIR ENTRAINED TO 5% TO 8%
WITH MAX. SLUMP OF 6". REINFORCED WITH
6X6 8/8 WWF AT MIDPOINT OF SLAB. 6" MIN
CLEAR COVER AT SLAB EDGE.
8 INCHES OF MDOT 21AA CRUSHED
LIMESTONE COMPACTED TO 95% OF
MAXIMUM DRY DENSITY AS DETERMINED BY
THE MODIFIED PROCTOR TEST
NOT TO SCALE
2'
CLAY WITH MIN. PLASTICITY INDEX (PI) OF 7. COMPACTED TO 95%
OF MAXIMUM DRY DENSITY AS DETERMINED BY THE MODIFIED
PROCTOR TEST WITHIN +/- 2% OF OPTIMUM MOISTURE CONTENT.
CLAY WITH MIN. PLASTICITY INDEX (PI) OF 7. COMPACTED TO 95%
OF MAXIMUM DRY DENSITY AS DETERMINED BY THE MODIFIED
PROCTOR TEST WITHIN +/- 2% OF OPTIMUM MOISTURE CONTENT.
CLAY WITH MIN. PLASTICITY INDEX (PI) OF 7. COMPACTED TO 95%
OF MAXIMUM DRY DENSITY AS DETERMINED BY THE MODIFIED
PROCTOR TEST WITHIN +/- 2% OF OPTIMUM MOISTURE CONTENT.
MDOT CLASS II SAND COMPACTED TO 95%
OF MAXIMUM DRY DENSITY AS DETERMINED
BY THE MODIFIED PROCTOR TEST.
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