MPCA LETTER 2013Minnesota Pollution Control Agency
520 Lafayette Road North � St. Paul, Minnewta 55155-4194 � 651-296-6300
800-657-3864 � 557-282-5332 TTY � www.pcastate.mn.us � EqualOpportunityEmployer
June 3, 2013
Mr. Greg Gray
Lake State Realty
6727 Valley Piace North
Crystal, MN 55427
RE: Petroleum Storage Tank Release Investigation and Corrective Action
Site: Highway 65 Apartments, 6341— 6342 Hwy 65 NE, Fridley, Anoka County 55432
Site ID#: LEAK 19114
Dear Mr. Gray:
The Minnesota Pollution Control Agency's (MPCA) Petroleum Remediation Program (PRP) has been
informed that there has been a release of petroleum from a storage tank that you own and/or operate.
PRP was developed to provide assistance as you investigate, and if necessary, clean up your petroleum
release. The MPCA appreciates your timely notification so this Site can be handled in an efficient
manner.
State laws require that persons legally responsible for storage tank releases notify the MPCA of the
release, investigate the extent of the release, and take any necessary actions to clean up the release. A
person is generally considered legally responsible for a petroleum tank release if the person owned or
operated the tank either during or after the release, unless specifically exempted under law. See Minn.
Stat. §115C.021(2012).
If development of this property or the surrounding area is planned, State laws require that persons
properly manage contaminated soil and/or water uncovered or disturbed even if they are not legally
responsible for the storage tank release(s). Developers and other interested parties must also
incorporate appropriate response actions to prevent the further spreading of contamination. To receive
MPCA review and approval of proposed response actions, please contact the Petroleum Brownfields
Program (PBP) at 651-296-6300 or at 1-800-657-3864, or visit their website at
http://www.pca.state.mn.us/fovp80a. If petroleum contamination is encountered during development
work, the Minnesota State Duty Officer should be notified immediately.
The MPCA requests you take steps to investigate, and if necessary, clean up the release in accordance
with MPCA guidance documents. The site investigation must fully define the extent and magnitude of
the soil and/or groundwater contamination caused by the release. The MPCA recommends you hire a
qualified environmental consulting firm to help you investigate and cleanup the contamination on your
site. A quali�ed consulting firm should have experience in performing investigations of contaminated
sites and in developing and implementing corrective actions.
Please be aware that the MPCA does not conduct the investigation or cleanup at your Site. The MPCA
provides guidance and technical assistance during the project and reviews the reports submitted by your
environmental consultant. However, the MPCA urges you to contact the MPCA project manager
whenever you have a question or concern regarding your project.
In 1987, the legislature established the Petroleum Tank Release Compensation Fund (Petrofund) to
reimburse responsible persons and volunteers (i.e., property owners not responsible for releases) who
take corrective action for a portion of their costs. The Petrofund is administered by the Petroleum Tank
Release Compensation Board (Petro Board), which is part of the Minnesota Department of Commerce.
Mr. Greg Gray
Page 2
For petroleum investigations, if you wish to have your costs considered for reimbursement, the
environmental consultant you hire must be registered with the Petro Board. A list of registered
contractors is available from the Petrofund staff. Please note that, under the Petro Board's rules (See
Minn. R. ch. 2890), you must solicit a minimum of two written competitive consultant proposals on a
form prescribed by the Petro Board to incur costs eligible for reimbursement and a minimum of two
written competitive contractor bids must also be obtained for each contractor service. To learn more
about the Petrofund reimbursement program contact Petrofund staff at 651-215-1775 or 1-800-638-
0418 (in greater Minnesota only) or review the information available at the following website at
htto://mn.gov/commerce/topics/Petrofund/. Please be aware that Petrofurrd reimbursement
determinations are made by Petrofund staff at the Department of Commerce. The determinations are
based on whether or not the work performed at a leak site was necessary for investigation and
corrective action, which is determined by MPCA staff, and whether or not the costs for that work were
reasonable, which is determined by Petrofund staff.
Your insurance may cover this release. However, your insurance coverage may be affected by how
quickly you notify your provider. Therefore, you should review your insurance plan and contact your
insurance carrier immediately after receiving this letter.
Please provide notification to the MPCA by submitting the enclosed Leaksite Ownership Form to the
MPCA project manager listed below. The Leaksite Ownership Form must be completed and submitted
within 30 days of your receipt of this letter to indicate whether you intend to proceed with the
requested investigation and/or corrective action. If you do not respond within this time frame, the
MPCA.will assume that you do not intend to comply. In this case, the MPCA Commissioner may issue an
enforceable or'der that will require you, as responsible party, to take corrective action. Failure to
cooperate with the MPCA in a timely manner may result in reduced reimbursement from the Petro
Board, see Minn. R. Ch. 2890. If you do not cooperate, the MPCA has the option of taking the corrective
actions on your behalf and recovering its costs.
If you have questions concerning this letter or need additional information, please contact me at 651-
757-2331 or e-mail andrew.eddy@state.mn.us. Please reference the above LEAK # in all
correspondence. If you are calling long distance, you may reach the MPCA by calling 1-800-657-3864.
Sincerely,
.��jLAndrew Eddy
Project Manager
Petroleum Remediation Section
Remediation Division
AJE:Is
Enclosures
cc: Debra Skogen, Clerk, Fridley
John Berg, Fire Chief, Fridley
Brad Fields, Anoka County Solid Waste Officer
Chris Loch, Carlson McCain, Inc., Maple Plain
�
Carlson
McCain ENVIRONMENTAL • ENGINEERING • LAND SURVEYING
June 10, 2013
Fi�idley Fire Department
Attn: Mi-. Matt Field – Fire Inspector
6431 University Avenue NE
Fridley, MN 55432
Re: General Excavation Report Worksheet (MPCA Guidance Document 3-02)
Highway 65 Apartments
6341-6342 Highway 65 NE
Fridley, MN 55432
MPCA LEAK # 19114
Dear Mr. Field:
Carlson McCain, Inc. (Carlson McCain), on behalf of Nay-Rox Partnership, has completed the enclosed
General Excavation Repoi�t Worksheet (MPCA Guidance Document 3-02) in regards to underground
storage tank (UST) removal activities conducted at the above-referenced Site.
If you have any questions, you may contact me at (952� 346-3913 oi� email cloch@cai-lsonmccain.com.
Sincerely,
Carlson McCain, Inc.
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--�_.
Chris Loch
Project Manager
Enclosure
cc: Mr. Richard Dempsey – Nay-Rox Partnership
Mr. Andrew Eddy – MPCA Project Manager
PO Box 429, 5300 Highway 12 • Maple Plain, MN 55359 • Tel 952-346-3900 • Fax 952-346-3901 • www.carlsonmccain.com
GENERAL EXCAVATION REPORT WORKSHEET
�MPCA GUIDANCE DOCUMENT 3-02�
Highway 65 Apartments
6341/6342 Highway 65 NE
Fridley, MN 55432
Carlson McCain Pro�ect #�60�-00
MPCfI Leak #19I 1 �
Prepared for:
Nay-Rox Partnership
Attn: Mr. Richard Dempsey
6727 Valley Drive North
Crystal, MN 55427
�Ji�yae 10, 2013
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Carlson
�
McCain
PO Box 429, 5300 Highway 12
Maple Plain, MN 55359
Tel 952-346-3900
Fax 952-346-3901
www.carlsonmccain.com
ENVIRONMENTAL • ENGINEERING • LAND SURVEYING
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M i n nesota Pol I ution
Control Agency
General Excavation Report Worksheet
Guidance Document 3-02
Complete the warksheet below to document excavation and treatment of petroleum contaminated soil
' removed prior to a Site Investigation and/or during tank removals and/or upgrades. If soil is excavated
as an MPCA-approved corrective action after a Site Investigation is conducted, complete Guidance
Document 3-02a Corrective Action Excavation Report Worksheet. Conduct excavations in accordance
� with Guidance Document 3-01 Excavation of Petroleuna Contaminated Soil. Please type or print clearly.
Do not revise or delete text or questions from this report forni.
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The excavation worksheet 3-02 deadline is 10 months from the date of receipt of the MPCA "Petroleum
Storage Tank Release Investigation and Corrective Action" letter. MPCA staff may establish a shorter
deadline for high priority sites.
PARTI:BACKGROUND
A. Site: Highway 65 Apartments B. Tank Owner/Operator: Nay-Rox Partnership
MPCA Site ID#: 00019114 Attn: Mr. Richard Denipsey
Street: 6341/6342 Highway 65 NE
' City, Zip: Fridley,lVIN 55432
County: Anoka
' C. Excavating Contractor: Dean's Tank, Inc.
� Contact: Dean Nething
Telephone: (763) 535-0194
Tank Contractor Certification Number: 475
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Mailing Address:
StreetlBox: 6727 Valley Drive North
City, Zip: Crystal, MN 55427
Telephone: (612) 275-1116
D. Consultant: Carlson McCain, Inc.
Contact: Chris Loch
Street/Box: P.O. Box 429
City, Zip: Maple Plain, 55359
Telephone: (952) 346-3913
E. Others on-site during site work (e.g., fire marshal, local officials, MPCA staff, etc.):
Mr. Matt Field — Fire Inspector (Fridley Fire Department)
F. Site Location Information: Attach Guidance Document 1-03a Spatial Data Reporting Forna if it has
' not already been submitted or will not be submitted as part of Guidance Document 4-06 Investigation
Report For»z.
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MPCA Guidance Document 1-03a (Spatial Data Reporting Form) is attached as Appendix A.
Guidance Document c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
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Note: If person other than tank owner and/or operator is conducting the cleanup, provide name, address,
and relationship to site on a separate attached sheet.
PART II: DATES
A. Date release reported to MPCA: May 24, 2013
B. Dates site work performed (tanks removed, piping removed, soil excavation, soil barings, etc.):
Work Performed
Carlson McCain Inc. (Carlson McCain) and Dean's Tank, Inc.
(Deans) personnel were on-site for the removal of one abandoned
1,000-gallon underground storage tank (UST) located at the
above referenced apartment property (Site). The removed UST
appeared in poor condition, due to surface pitting, rusting and
several "dime-sized" holes observed near the bottom of the tank.
Photographs #1 through #3, illustrating the Site and the removed
UST are attached as Appendix B: Carlson McCain personnel
collected a total of six soil samples for on-site field screening
purposes. Samples were collected alongside and directly beneath
the removed UST. Field screening activities, including visual and
olfactory observations, identifed petroleum impacted soil within
the former tank basin, directly below the removed UST. Tank
bottom samples (B-1 and B-2), collected from directly below each
end of the removed UST and within saturated sandy soils, were
submitted to a certified laboratory for analysis: It should be
noted that a groundwater sample was not collected because of
limited groundwater accumulating within the former tank basin.
The Minnesota State Duty Of�cer was subsequently notified of a
release at the Site (Duty Officer report #134011). The former
UST basin, Site characteristics and soil sampling locations are
visually depicted on Figure 2, attached.
Date
May 24, 2013
PART III: SITE AND RELEASE INFORMATION
A. Describe the land use and pertinent geographic features within 1,000 feet of the site.
(i.e. residential property, industrial, wetlands, etc.)
The Site is located at 6341/6342 Highway 65 NE in Fridley, Minnesota. The Site is currently
developed as multi-family residential, consisting of an apartment building. The removed UST
was located along the east side of the apartment building (Figure 2). The Site is adjoined by
mixed residential and light commercial properties to the north; residential homes to the east;
light commercial properties to the south; and Highway 65 followed by commercial properties
to the west. The nearest surface water is Moore Lake located approximately 1,685 feet (0.32
mile) to the southwest of the Site.
Guidazice Document c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
Page 3
B. Provide the following information for all tanks removed and any remaining at the site:
Table 1.
Tank # Tank ** UST or Capacity Contents Year Tank Condition of Tank
Material AST (gallons) (product installed Statusx
t e)
001 Steel UST 1,000- Fuel Oil Unknown Removed Poor condition,
gallons (5/24/13) pitting & d'une-sized
holes
*Indicate: removed (date), abandoned in p[ace (aate�, or currenaiy usea, upgruueu cur�rc, trt�tutcuciun u�
new tank. ** F for fiberglass or S for Steel
Notes: UST = underground storage tank; AST = aboveground storage tank.
Piping Matei•ial (check all that apply): � Steel, 0 Fiberglass, 0 Flexible Plastic, ❑ Copper, ❑ Other
C. Describe the location and status of the other components of the tank system(s) (i.e., transfer locations,
valves, piping and dispensers) for those tanks listed above. � � �
A buried fill pipe, located directly above the center of the UST was removed. The steel vent
and product lines were also removed. The piping appeared in good condition.
D. Identify the source(s) of the release or contamination encountered. Only check those options that
were verified, if source� is unknown check Other and describe:
❑ Piping, �Tank, ❑ Dispenser, ❑ Pump/Turbine, ❑ Delivery Problem, ❑ Other
Several "dime-sized" holes w.ere observed near the. bottom of the UST. The attached
photographs #2 and #3 visually depicts the condition of the removed UST. �
' E. Identify the cause of the release (tank andlor piping).
Check all that apply: � Corrosion, ❑ Install Problem, ❑ Spill, 0 Unknown,
❑ Mechanical or Physical Damage, ❑ Other
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F. Identify the method the release was detected.
Check all that apply: �Removal, 0 Line Leak Detection, Q Tank Leak Detection,
� VisuaVOlfactory, ❑ Site Assessinent, ❑ Other:
G. Identify any surface soil contamination. N/A
H. What was the volume.of the release? (if lalown): Unknown gallons
I. Historic contamination present (unknown origin?). ❑ Yes, � No
J. When did the release occur? (if known): Unknown
K. Describe source of on-site drinking water.
The Site and neighboring residential and commercial properties receive municipal water from
the City of Fridley.
Guidv�ce Document c-prp3-02: February 2010
Petroleum Remediation Prograni
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
Page 4
L. Has the site evei•, at any point had an E-85 tank? ❑ Yes, � No
PART IV: EXCAVATION INFORMATION
A. Dimensions of excavation(s): Length = 12 feet; Width = 7 feet; and Depth = 10 feet
B. Original tank backfill material (sand, gravel, etc.), if applicable: Srown, well graded sand (SW)
C. Native soil type (clay, sand, etc.): Light brown, poorly graded sand (SP)
D. Quantity of contaminated soil removed for treatment (cubic yards): None
(Indicate on the site map where the petroleum contaminated soil was excavated)
How many cubic yards of the removed soil was petroleurn saturated? N/A
(Indicate on the site map where the petroleuin saturated soil was excavated)
[Note: If the volume removed is more than allowed in Guidance Document 3-O 1 Excavation of
Petroleunz Contaminated Soil, please document MPCA staff approval.]
E. Were new tanks and/or piping and dispensers installed? (yes/no) If yes, what volume of
contaminated soil was excavated to accommodate the installation of the new tanks and piping?
New tanks, piping and dispensers were not installed.
F. If contaminated soil was removed to accoinmodate the installation of new tanks and/or piping, show
' your calculations for the amount of soil removal allowed using Table 3 in Guidance Document 3-01
Excavation of Petroleum Contaminated Soil.
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N/A
G. Was groundwater encountered or a suspected perched water layer or was there evidence of a
seasonally high groundwater table (i.e. mottling)? (yes/no) At what depth? 10 feet -
Saturated sandy soil was encountered during tank removal activities at a depth of
approximately 10 feet below ground surface (bgs).
H. If groundwater was not encountered during the excavation, what is the expected depth of ground
water?
The expected depth to groundwater is within the encountered saturated sandy soil
(approximately 10 feet bgs).
I. Additional investigation to determine the need for a Limited Site Investigation is necessary at sites
with sandy or silty sandy soil, a water table within 25 feet of the ground surface, and visual or other
evidence of soil remaining contamination. See Table 2 in Guidance Document 3-01 Excavation of
Petroleuna Contaminated Soil. If a soil boring is necessary, describe the soil screening and analytical
results. Attach the boring logs and laboratory results to this report.
Guidance Document c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
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J. If no soil boring was performed, explain.
A soil boring was not advanced within the UST basin. It appears a standard scope Limited Site
Investigation (LSn is necessary to assess the horizontal and vertical extent of soil and
groundwater contamination. Field screening activities, including visual and olfactory
observations, identified the presence of petroleum contamination along the bottom of the
former UST basin and impacting the shallow groundwater table.
K. If groundwater was encountered or if a soil boring was conducted, was there evidence of
groundwater contamination? (yes/no) Describe this evidence of contamination, e.g., free product
(specify thickness), product sheen, groundwater in contact with petroleum contaminated soil, water
analytical results, etc. Note: If you observe free product, contact MPCA staff immediately, as
outlined in Guidance Document 2-02 Free Product.• Evaluation and Recovery.
Petroleum impacted soil was observed to be in contact with saturated sandy soil (water table).
It should be noted that free product nor a petroleum sheen was observed within the saturated
soil.
L. Was bedrock encountered in the excavation? ( Qyes/ �no) At what depth? N/A
M. Were other unique conditions associated with this site? (❑yes/ �no) If so, explain. N/A
Guidance Document c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
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PART V: SAMPLING INFORMATION
A. Briefly describe the field screening methods used to distinguish contaminated from uncontaminated
soil:
Soil samples collected for on-site field screening activities were placed in polyethylene bags.
The bag headspace analysis was completed with a MiniRAE photoionization detector (PID)
equipped with 10.6 eV lamp. Each bag was half-filled with soil and was closed for a minimum
of 10 minutes and then was shaken for 15 seconds before the probe tip was inserted into the
bag. The highest meter reading by the PID within �ve seconds was then recorded. The PID
was calibrated on-site prior to use with compressed isobutylene gas to read parts-per-million
volume/volume of benzene vapors. In addition, visual and olfactory observations were used to
determine contaminated from uncontaminated soil.
B. List soil vapor headspace analysis results collected during excavation of tanks, lines and dispensers,
valves, and transfer locations. (i.e., soils left in place when excavation is complete). Code the
samples with sampling.depths in parentheses as follows: sidewall samples S-1 (8 feet), S-2 (4 feet),
. etc.; bottom samples B-1 (13 feet), B-2 (14 feet), removed soil R-1 (4 feet), R-1 (8 feet), etc.;
stockpile samples SP-1, etc; line samples L-1, L2, etc.; transfer locations T-1 (4 feet), T-1 (8 feet),
etc.; dispensers D-1 (4 feet), etc. Be sure the sample codes correspond with the site map in part
VI, below. �
Sample Soil Reading
Code Type ppm
S-1 (4') Sand (SW) 0.0
S-2 (4') Sand (SW) 0.0
S-3 (5') Sand (SW 0.0
Sample Soil Reading
Code Type ppm
5-4 (6') Sand (SW) 0.0
B-1 (10') Sand (SP) 103
B-2 (10') Sand (SP) 24.9
C. Was the "removed soil" placed back into the excavation basin? (�yes/ Ono)
, If no, please complete Part VIII: Soil Treatment Information section. If yes, a Limited Site
Investigation is necessary (see Guidance Document 4-01 Soil and Ground Water Assessments
Performed during Site Investigations).
' D. Briefly describe the soil analytical sampling and handling procedures used:
' Soil samples (B-1 and B-2) were collected beneath the south and north ends of the removed
UST for laboratory analysis, respectively. The tank basin soil samples were collected at depths
of 10 feet bgs, within saturated, light brown, colored, poorly graded sand (SP). The soil
' sampling locations are visually depicted on Figure 2, attached. The collected soil samples were
submitted to Test America, Inc. (Test America) for laboratory analysis of benzene, toluene,
ethylbenzene, xylenes (BTEX) and diesel range organics (DRO).
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To minimize cross contamination of samples, clean disposable gloves and sampling utensils
were used while obtaining samples for analytical testing. Soil samples were collected in
laboratory-supplied, test-specific sample containers, then stored and shipped in ice-filled
containers along with their chain of custody form until they were relinquished to the
laboratory.
Guidance Document c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
Page 7
E. List below all soil sample analytical results from bottom and side wall samples collected after
excavation of tanks, lines and dispensers, valves, and transfer locations (i.e., soils left in place when
excavation is complete). Code the samples with sampling depths in parentheses as follows: sidewall
samples S-1 (8 feet), S-2 (4 feet), etc.; bottom samples B-1 (13 feet), B-2 (14 feet), removed soil R-1
(4 feet), R-1 (8 feet), etc.; stockpile samples SP-1, etc; line samples L-1, L2, etc.; transfer locations
T-1 (4 feet), T-1 (8 feet), etc.; dispensers D-1 (4 feet), etc.; Be sure the sample codes correspond
to the site map required in part VI.
Sample GRO/ Benzene Ethyl- Toluene Xylenes MTBE Lead
Code DRO mg/kg benzene mg/kg mg/kg mg/kg mg/kg
mg/kg mg/kg
B-1 (10') NA/1,510 <0.127 0.142 <0.127 <0382 NA NA
B-2 (10') NA/27.3 <0.120 <0.120 <0.120 <0359 NA NA
MeOH Blank NA/NA <0.100 <0.100 <0.100 <0.300 NA NA
Note: Attach copies of laboratory reports and chain of custody fonns.
The laboratory analytical report is attached as Append�x C. GRO = gasoline range organics; DRO
_. diesel range organics; MTBE = methyl-tert-butyl-ether; NA = not analyzed; and mg/kg =
milligrams per kilogram.
PART VI: FIGURES �
Attach the following figures to this report: �
1. Site location map. �
2. Site map(s) drawn to scale illustrating the following: �
a. Location of all present and former tanks, piping, and dispensers;
b. Location of surface soil contamination •
c. Location of other structures (buildings, canopies, etc.);
d. Adjacent city, township, or county roadways;
e. Dimensions of excavation(s), including contour lines (maximum 2-foot contour intervals) to
represent the depths of the final excavation(s);
£ Location of soil screening samples (e.g. R-1), soil analytical samples (e.g., S-1 or B-1), and
any soil borings (e.g., SB-1). Also, attach all boring logs. ��
g. North arrow, bar scale and map legend. �
h. Provide location of any on-site water wells. If on-site water wells exist, please provide well
logs and/or construction diagrams.
i. Locations of new tanks, piping and dispensers, if installed.
Guidance Document c-prp3-02: February 2010
Petroleum Remediation Pro�ram
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
Page 8
PART VII: CONCLUSIONS AND RECOMMENDATIONS
Recommendation for site: ❑site closure
�additional investigation
Justify the recommendations for the site. If no further action is necessary, the MPCA staff will review
this report following notificat0l ion of soil treatment.
, Carlson McCain recommends a standard scope of work LSI, which would include the
advancement of up to five direct push soil borings within and around the former tank basin
(source area) to assess the vertical and horizontal extent of soil and groundwater contamination.
' In addition, soil gas samples should be collected at the depth of the Site building's and surrounding
properties basement footings to evaluate the potential for vapor intrusion to the Site apartment
building and nearby residential homes. Subsequent investigation reporting would follow.
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The petroleum release appears to be the result of UST corrosion. Pitting and several "dime-sized"
holes were observed near the bottom of the removed UST. The UST has been out of service since
the conversion to natural gas .in the 1970's. Field screening activities and laboratory analysis of
soil samples collected below each end of the removed UST identified petroleum impacts to native,
saturated sandy soil encountered below the tank. Laboratory analysis of tank bottom soil samples
B-1 (10') and B-2 (10') indicated DRO and ethylbenzene concentrations above laboratory detection
i�m,ts.
Based on an evaluation of the potential threats as they relate to the petroleum constituent
' concentrations detected within soil samples B-1 (10') and B-2 (10'), petroleum impacted soil in
contact with shallow groundwater and confirmatory information regarding the MPCA general
policy, a standard scope LSI is recommended:
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Impacted groundwater tlzat /:as or may affect human Izealtlt: Shallow groundwater
was encountered during tank removal activities. Saturated sandy soil was
encountered at an approximate depth of 10 feet bgs. Because impacted soil appears
in contact with the shallow groundwater table, an LSI is necessary to evaluate and
potentially define the extent of groundwater contamination.
Led or ntay lead to dangerous conditions due to petroleum vapor: The potential for
vapor intrusion to the Site building (apartment complex) may currently exist.
Moderate concentrations of DRO were detected in soil samples collected below the
removed UST, located along the east side of the Site apartment building. Therefore,
Carlson McCain recommends soil gas samples be collected within the vicinity of the
former UST basin, towards the Site building and toward adjoining residential
properties to assess potential vapor intrusion impacts.
• Affect or may affect surface water quality: The threat for surface water impacts are
' considered low due to the distance between the former tank basin and nearby surface
water features. The nearest surface water is Moore Lake located approximately
1,685 feet (0.32 mile) to the southwest of the Site. The concentrations of petroleum
� constituents detected in soil below the removed UST is likely insufficient to migrate a
distance that would impact nearby surface waters. However, the vertical and
horizontal extent of contamination is unknown.
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Guidance Document c-prp3-02: February 2010
Petroleum Remediation Prob am
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
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• Caused or may cause dermal contact: The potential for direct contact is considered an
insignificant threat due to the contamination being detected at depths of
approximately 10 feet bgs within the former tank basin.
Based on Site conditions with respect to MPCA general Guidance, Carlson McCain
recommends the standard scope of work LSI be completed to assess the vertical and
horizontal extents of petroleum impacts discovered during abandoned UST removal
activities.
PART VIII: SOIL TREATMENT INFORMATION
A. Soil treatment method used (thermal, land application, composting, other). If you choose "other"
specify treatment method: N/A
B. Location of treatment site/facility: N/A
C. Date MPCA approved soil treatment (if thennal treatment was used, indicate date that the MPCA-
perr�itted thennal �treahnent facility agreed to accept soil): N/A
D. Identify the location of stockpiled contaminated soil:
N/A
Guidance Docmnent c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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General Excavation Report Worksheet
Page 10
PART IX: CONSULTANT (OR OTHER) PREPARING THIS REPORT
By signing this document, I/we acknowledge that we are subnaitting this document on behalf of and as
agents of the responsible person or volunteer for this leak site. I/we acknowledge that if infornzation in
this document is inaccurate or inco�nplete, it will delay the completion of remediation and nzay harna the
environment and may result in reduction of reinabursenzent awards. In addition, I/we acknowledge on
behalf of the resporzsible person or volunteer for this leak site that if this docunaent is determined to
contain a false naaterial statement, representation, or certification, or if it omits material information,
the responsible person or volunteer may be found to be in violation of Minn. Stat. � 11 S. 075 (1994) or
Minn. 7000. 0300 (Duty of Candor), and that the responsible person or volunteer may be liable for civil
penalties.
MPCA staff are instructed to reject unsigned excavation reports or if the report form has
been altered.
Name and Title:
Christopher J. Loch
Project Manager
Barbara A. Ryan, P.G.
Project Geologist
Company and mailing address
Signature:
.- ._—�
�==---" _����--�'�-�- �_..__
. ��'`"`i' ���`~'
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Carlson McCain, Inc.
P,O. Box 429
Maple Plain, MN 55359
Phone: 952-346-3913
Fax: 952-346-3901
Date signed:
6/10/13
6/10/13
If additional investigation is not necessary, please mail this form and all necessary attachments to the
MPCA project manager. If additional investigation is necessary, include this form as an appendix to
Guidance Document 4-06 Investigation Report Fornz. MPCA staff will not review excavation reports
indicating a limited site investigation is necessary unless the limited site investigation has been
completed.
Web pages and phone numbers
MPCA staff http://pcastate.mn.us/pca/staff/index.cfm
MPCA toll free 1-800-657-3864
Petroleum Remediation Program web page
http://��vrvw.pca. state.mn.us/proarams/lust�.html
MPCA Infor. Request http://www.pca.state.mn.us/about/inforequest.html
MPCA Petroleum Brownfields Program
http://www.pca.state.mn.us/pro}rams/vpic p.html
PetroFund Web Page http�//ww�v state nu� us/cQi-Uin/portalhnn/'Lsp/content.do?id=-
536881377&a�ency=Commerce
PetroFund Phone 651-297-1119, or 1-800-638-0418
State Duty Officer 651-649-5451 or 1-800-422-0798
Upon request, this document can be made available in other tormats, including 13raille, iarge prmt ana auuto tape. i i Y users caii o� ii�n�-�s.s�
or 1-800-657-3864 (voice/TTY).
Printed on recycled paper containing at least 10 percent fibers from paper recycled by consumers.
Guidance Document c-prp3-02: February 2010
Petroleum Remediation Program
Minnesota Pollution Control Agency
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Petroleum Remediation Pro�ram
Minnesota Pollution Control Agency
http://www.pca.state.mn.us/programs/lust_p.html
' Spatial Data Reporting Form
Guidance Document 1-03a
(For complete instructions, see Guidance Document 1-03.)
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Part 1. Background
Has a site location data point been submitted for this site (circle/highlight)? YES or NO
If yes, you do not need to complete Part 2 of this form but should complete Part 3 if there are
additional site features to report. This form can be submitted electronically if desired (e.g., as
an e-mail attachment to the project manager).
' MPCA Site ID: LEAK00019114
Site Name: Highway 65 Apartments
Data Collection Date: June 6, 2013
' Name of Person Who Collected Data: Chris Loch
Organization Name: Carlson McCain, Inc.
Organization Type: Environmental Consulting Firm
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Part 2. Site Location (use one of the three spatial data reporting formats provided)
Point Description: Center of former underground �torage tank (UST)
Collection Method: Map Interpolation
Datum (circle/highlight): NAD83
1) Longitude (dd mm ss.ss): 93° 14' 32.65" Latitude (dd mm ss.ss): 45° OS' 00.66"
2) Longitude (dd.dddddd): Latitude (dd.dddddd):
3) UTM - X(Easting): UTM - Y(Northing):
UTM Zone:
Guidance Document c-prpl-03a: Apri12005
' Petroleum Remediation Program
Minnesota Pollution Control Agency
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Spatial Data Reporting Form
Page 2
Part 3. Other Site Features
Point Description:
Collection Method:
Datum (circle/highlight): WGS84
1) Longitude (dd mm ss.ss):
2) Longitude (dd.dddddd):
3) UTM - X (Easting):
UTM Zone:
Point Description:
Collection Method:
Datum (circle/highlight): WGS84
1) Longitude (dd mm ss.ss):
2) Longitude (dd.dddddd):
3) UTM - X (Easting):
UTM Zone:
Point Description:
' Collection Method:
Datum (circle/highlight): WGS84
1) Longitude (dd mm ss.ss):
' 2) Longitude (dd.dddddd):
3) UTM - X (Easting):
UTM Zone:
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Point Description:
Collection Method:
Datum (circle/highlight): WGS84
1) Longitude (dd mm ss.ss):
2) Longitude (dd.dddddd):
3) UTM - X (Easting):
UTM Zone:
Point Description:
Collection Method:
Datum (circle/highlight): WGS84
1) Longitude (dd mm ss.ss):
2) Longitude (dd.dddddd):
3) UTM - X (Easting):
UTM Zone:
NAD83
NAD83
Latitude (dd mm ss.ss):
Latitude (dd.dddddd):
UTM - Y (Northing):
Latitude (dd mm ss.ss):
Latitude (dd.dddddd):
UTM - Y (Northing):
NAD83
Latitude (dd mm ss.ss):
Latitude (dd.dddddd):
UTM - Y (Northing):
I►: �:
NAD83
Latitude (dd mm ss.ss):
Latitude (dd.dddddd):
UTM - Y (Northing):
Latitude (dd mm ss.ss):
Latitude (dd.dddddd):
UTM - Y (Northing):
Guidance Document c-prpl-03a: Apri12005
Petroleum Remediation Program
Minnesota Pollution Control Agency
Ta�zk Removal flctivities
Higlzze�ay 6.5 A�artments —�+ ridley, 111N
,�
MPCA I eak No. I9I I�
� ��� j �
� � _ ` h�'t'�y ~ , � � � � � f } � � ,� � �
�
;�♦'' � . . � � . iiR \ F% c "�� i
,.� � �"§'` .� J -
_ .. �._. ::,� ,
Pl�oto 1— V ic�v of tl�c east side of the Site biul�Iiu�; au� �uicicrbrou►��i �tora�;c tai�l:
(UST) basin. Bro�vn, well graded sand (SW) surrounded the former 1,00o-gallon
fuel oil UST.
—.,�� a "1 j�ill ��
_ �{� ii� �+���p,,
� � ,�" �
� V �
ti. �
„� ��' ' . • • . ;.. ,.
� � �
,,. �
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,
�
� �'"
.. „ �
. . ..... . , .'.�. ..). . , _. °" � . �...:-
Photo 2— Visually depicl� ti►c rcinovcd 1,000-gallon (6�1,"' �l�ametcr l�y 72" long)
fuel oil UST. The UST appeared in very poor condition, exhibiting severe
rusting, pitting and several "dime-sized" holes near the bottom of the tank.
Ca�-lso�a 1'�7cCai�t, I�ac. Pa�;e 1 of2
Tank Removal flciivities MPCIl Leah No. 1911 �
Highz�ay 6,� ll�a7•tments — Fridley, MN
���" . ' :. _ , - _,� �
.�,
;�: : � `'- � r� � .� w��� �f, ���
> `�i`` Z �✓ l � ^ ��
r� � �� •
� �• '•� • ti'., _��' •M{� '' O ` �. .
�L 4 � �+' � ..
r'
: ��� ;.' �;.- k� i
, �`� * �� ..� � . •.�.
�
y, i' » ; k r .,
a
�� � ���) d�� .. ���:� � d,� ��
t � � ,�,� ..Y` } ' r 1
'* '�. � r i�. �''i'��i� f�
�" �.. %'r
� ,,+ �,.; �e ,;` .
�� i'r� - : ' �'" �.�. � � �' . ' �.�
Pa � � � �� :�, � :.w5,;.. . ; . -
�..� y - .`rt � r'.; t.i',"'J -
``i;Y 'Y �- . � �� ��'� 'b,a. '�'•. ; +�'
✓ � ,. i
;�.�.
� � � * �
x fv'
� � � : r'�;.. � ,
:� `d'sa �." � � i i S,nL � ;
' � �. . , �� 4 ��� ��
„ „ -
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y .
...3"• . . ' .z . .
�:. `
.. �
' . t'��`.�,.�:«� �I�W{il��ii� :_:�
Photo 3— Illustrates the holes observed along the southern bulkhead of the
removed 1,000-gallon fuel oil UST.
Carlson 1'�7cCain, I�rc.
Pczge 2 of 2
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THE LEA�ER IN ENVIRONMENTAL TESTING
ANALYTICAL REPORT
TestAmerica Laboratories, Inc.
TestAmerica Cedar Falls
704 Enterprise Drive
Cedar Falls, IA 50613
Tel: (319)277-2401
TestAme��ica Job ID: 310-8660-1
TestAmerica Sample Delivery Group: 4604-00
Client Project/Site: 4604-00
For:
Carlson McCain, Inc.
530Q Highway 12
Maple Plain, Minnesota 55359
Attn: Mr. Chris Loch
_ �
Authorized for release by:
6/4/2013 4:04:45 PM
Derrick Klinkenberg, Project Manager I
derrick.klinkenberg@testamericainc.com
This report has been electronically signed and authorized by the signatory. Efecfronic signature is
intended to he the legally binding equivalent of a traditionally handwrrtfen signature.
Results relafe only to fhe rtems tested and the sample(s) as received by the laborafory.
�
Client: Carison McCain, Inc.
P roj e ct/S ite: 4604-00
'
TestAmerica Job ID: 310-8660-1
SDG: 4604-00 'P �
Table o on en s
CoverPage .............................................. �
Table of Contents . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
Case Narrative ........................................... 3
Sample Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
Detection Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5
Clien� Sample Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6
Definitions ............................................... 9
Surrogate Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10
QC Sample Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11
QC Association ........................................... 13
Chronicle ................................................ 14
Certification Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 15
Method Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 16
Chain of Custody . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17
Receipt Checklists . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 19
TestAmerica Cedar Falls
Page 2 of 19 6/4/2013 '
Client: Carlson McCain, Inc.
Project/S ite: 4604-00
Job ID: 310-8660-1
Laboratory: TestAmerica Cedar Falis
Narrative
�a�e Idarrative
Job Narrative
310-8660-1
TestAmerica Job ID: 310-8660-1
SDG: 4604-00
Comments
No additional comments.
Receipt
The samples were received on 5/25/2013 9:20 AM; the samples arrived in good condition, properly preserved and, where required, on ice.
The temperature of the cooler at receipt was 1.7° C.
GC VOA
Method(s) WI-GRO: Surrogate recovery for the following sample(s) was outside control Iimits: B-1 (10') (310-8660-1). Evidence of matrix
interference is present; therefore, re-extraction and/or re-analysis was not performed.
No other analyticai or qualiry issues were noted.
GC Semi VOA �
Method(s) WI-DRO: The laboratory control sample (LCS) and / or the laboratory control sample duplicate (LCSD) for batch 310-14692
recovered outside control limits. Re-analysis has been performed, results confirmed. �
No other analytical or quality issues were noted.
General Chemistry �
No analytical or quality issues were noted.
Organic Prep • •
No analytical or quality issues were noted.
VOA Prep
No analytical or quality issues were noted.
Page 3 of 19
TestAmerica Cedar Falls
6!4/2013
a�
Client: Carlson McCain, Inc.
Project/S ite: 4604-00
Lab Sample ID
310-8660-1
310-8660-2
310-8660-3
Client Sample ID
B-1 (10')
B-2 (10')
MeOH Blank
Sample Summary
Page 4 of 19
Matrix
Soil
Soil
Soil
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TestAmerica Job ID: 310-8660-1 �
S DG: 4604-00
_ Collected Received �
05/24/13 10:25 O5/25/13 09:20
05/24/13 10:30 O5/25/13 09:20
O5/24/13 10:35 OS/25/13 09:20
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TestAmerica Cedar Falis ,
6/4/2013 '
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Client: Carlson McCain, Inc.
Project/S ite: 4604-00
Client Sample ID: B-1 (10')
�Analyte
Ethylbenzene
�Diesel Range Organics (DRO)
Client Sample ID: B-2 (10')
CAnalyte
Diesel Range Organics (DRO)
Client Sample ID: MeOH Blank
� No Detections.
Detection Summary
Result Qualifier RL MDL Unit
0.142 0.127 mg/Kg
1510 ' 48.5 m9�K9
Result Qualifier
27.3 `
This Detection Summary does not include radiochemical test results.
RL MDL Unit
4.15 mg/Kg
Page 5 of 19
TestAmerica Job ID: 310-8660-1
SDG: 4604-00
Lab Sample ID: 310-8660-1
DilFac D Method PrepType
1 � WI-GRO Total/NA
10 � WI-DRO Total/NA �
Lab Sample ID: 310-8660-2
Dil Fac D Method Prep Type
1 � WI-DRO Total/NA
Lab Sample ID: 310-8660-3
TestAmerica Cedar Falls
6/4/2013
Client Sample Results
Client: Carison McCain, Inc.
P roj e ct/S ite: 46 04-00
Client Sample ID: B-1 (10')
Date Coilected: 05/24/13 10:25
Date Received: 05/25113 09:20
Method: WI-GRO - Wisconsin - Gasoline Range Organics (GC)
Analyte Result Qualifier
Benzene <0.127
Ethylbenzene 0.142
Toluene `�•127
Xylenes, Total <0.382
Surrogate %Recovery Quafifer
4-Bromofluorobenzene (Surr) 1 Z9 x
Method: VIII-DRO - Wisconsin - Diesel Range Organics (GC)
Analyte Result Qualifier
Diesel Range Organics (DRO) 1510 '
RL
0.127
0.127
0.127
0.382
Limits
80 _ 120
RL
48.5
Page 6 of 19
MDL Unit
mg/Kg
mg/Kg
mg/Kg
mg/Kg
MDL Unit
mg/Kg
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TestAmerica Job ID: 310-8660-1 '
SDG: 4604-00
Lab Sample ID: 310-8660-1
fNatrix: Soil '
Percent Solids: 77.3
D Prepared Analyzed Dil Fac
� 05/31/13 08:53 OS/31/13 13:39 1
� OS/31/13 08:53 OS/31/13 13:39 1 •
� 05/31113 08:53 OS/31/13 13:39 I
� 05/31/13 08:53 OS/31l13 13:39 1 '
Prepared Analyzed Dil Fac
05/31/13 08:53 05/31/13 13:39 1 ,
D Prepared Analyzed Dil Fac
� OSl29l1317:51 06/02/1314:17 10 '
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TestAmerica Cedar Falls �
6/4/2013 �
Clieni Sample Results
Client: Carlson McCain, Inc.
Proj ect/S ite: 4604-00
Client Sample ID: B-2 (10')
Date Collected: 05/24/13 10:30
Dafe Received: 05/25l13 09:20
Method: WI-GRO - Wisconsin - Gasoline Range Organics (GC)
Analyte Result Qualifier
Benzene <0.120
Ethylbenzene <0.120
Toluene <0.120
Xylenes, Total <0.359
Surrogafe %Recovery Qualifier
4-Bromofluorobenzene (Surr) 96
Method: WI-DRO - Wisconsin - Diesel 62a�ge Organics (GC)
Analyte Result Qualifier
Diesel Range Organics (DRO) 27.3 °
RL
0.120
0.120
0.120
0.359
Limits
80-120
RL
4.15
Page 7 of 19
TestAmerica Job ID: 310-8660-1
S DG: 4604-00
Lab 5ample ID: 310-8660-2
Matrix: Soil
Percent Solids: 82.5
MDL Unit D Prepared Analyzed
mg/Kg � OSl31/13 08:53 05/3�/13 14:06
mg/Kg � OS/31/13 08:53 OS/31/13 14:06
mg/Kg � 05/31/1308:53 OS/31/�314:06
mg/Kg '� OS/31/13 08:53 O5/31/13 14:06
Prepared Analyzed
05/31/13 08:53 05/31/13 14:06
MDL Unit
mg/Kg
Dil Fac
1
1 •
1
1
Dil Fac
1
D Prepared Analyzed Dil Fac
� 05/29/13 17:51 OS/31/13 03:00 1
TestAmerica Cedar Falls
6(4/2013
Client Sample Results
Client: Carlson McCain, Inc.
P roj e ct/S ite : 46 04-00
Client �ample ID: MeOH Blank
Date Collected: 05/24/13 10:35
Date Received: 05125/13 09:20
Method: WI-GRO - Wisconsin - Gasoline Range Organics (GC)
Anaiyte Result Qualifier
Benzene <0.100
Toluene <0.100
Ethylbenzene <0.100
Xylenes, Total <0.300
Surrogate %Recovery Qualifier
4-Bromofluorobenzene (Surr) 94
RL
0.100
0.100
0.100
0.300
Limits
80_120
Page 8 of 19
'
TestAmerica Job ID: 310-8660-1 '
S DG: 4604-00
Lab Sample ID: 310-8660-3
Mafrix: Soil
MDL Unit D Prepared Analyzed
mg/Kg 05/30/13 08:34 05/30/13 13:41
mg/Kg 05/30/13 08:34 05/30/13 13:41
mg/Kg 05/30/13 08:34 O5/30/13 13:41
mg/Kg 05/30/13 08:34 OS/30/13 13:41
Prepared Analyzed
05/30/13 08:34 05/30/13 13:41
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Dil Fac
1
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1 '1
Dil Fac
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TestAmerica Cedar Falls '
6/4/2013 '
Definitions/Glossary
Client: Carlson McCain, Inc.
Project/S ite: 4604-00
Qualifiers
GC VOA
Qualifier Qualifier Description
)( Surrogate is outside control limits
GC Semi VOA
Qualifier Qualifier Description
* LCS or LCSD exceeds the control limits
Glossary _
Abbreviation These commonly used abbreviations may or may not be present in this report.
❑ Listed under the "D" column to designate that the result is reported on a dry weight basis
%R Percent Recovery
CNF Contains no Free Liquid
DER Duplicate error ratio (normalized absolute difference)
DL, RA, RE, IN Indicates a Dilution, Re-analysis, Re-extraction, or additional Initial metals/anion analysis of the sample
DLC Decision level concentration
MDA Minimum detectable activity
EDL Estimated Detection Limit �
MDC Minimum detectable concentration
MDL Method Detection Limit •
ML Minimum Level (Dioxin)
ND Not detected at the reporting limit (or MDL or EDL if shown)
PQL Practical Quantitation Limit
Q� Quality Control
RER Relative error ratio
RL Reporting Limit or Requested Limit (Radiochemistry)
RPD Relative Percent Difference, a measure of the relative difference between hvo points
TEF Toxicity Equivalent Factor (Dioxin)
TEQ Toxicity Equivalent Quotient (Dioxin)
Page 9 of 19
TestAmerica Job ID: 310-8660-1
SDG: 4604-00
TestAmerica Cedar Falls
6/4/2013
�
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Surrogate Summary
Client: Carlson McCain, Inc. TestAmerica Job ID: 310-8660-1 '
ProjecUSite: 4604-00 SDG: 4604-00
Method: WI-GRO - Wisconsin - Gasoline Rang� Organics (GC)
YVlatrix: Soil Prep Type: TotallNA '
Percent Surrogate Recovery (Acceptance Limits)
BFB
Lab Sample ID Client Sample ID (80-120) _ _ '
310-8660-1 B-� (�0') �ZgX
310-8660-2 B-2 (10') 96
310-8660-3 MeOH Blank 94
Surrogate Legend
BFB = 4-Bromofluorobenzene (Surr) i
ENlethod: WI-GRO - Wisconsin - Gasoline Range Organics (GC)
Matrix: Solid Prep Type: To4a11NA
Percent Surrogate Recovery (Acceptance limits) '
BFB
Lab Sample ID qient Sample ID (80-120) _ __ _
LCS 310-14732/2-A Lab Control Sample 100 '
LCS 310-14897/2-A Lab Control Sample 96
LCSD 310-14732/26-A Lab Control Sample Dup g$
LCSD 310-14897/25-A Lab Control Sample Dup 96
MB 310-14732/1-A Method Blank 100 '
MB 310-14897/1-A Method Blank 97
Surrogate Legend _
BFB = 4-Bromofluorobenzene (Su«) ,
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Page 10 of 19 6/4/2013 ,
QC Sample Results
Client: Carlson McCain, Inc.
P roj e ct/S ite: 4604-00
Method: WI-GRO - Wisconsin - Gasoline Range
Lab Sample ID: IVIB 310-1473211-A
Matrix: Solid
Analysis Batch: 14739
MB MB
Analyte Result Qualifier
Benzene <0.0976
Ethylbenzene <0.0976
Toluene <0.0976
Xylenes, Total <0293
MB MB
Surrogate %Recovery QualiFer
4-Bromofluorobenzene (Surr) 100
Lab Saonple ID: LCS 310-144�3212-A
Matrix: So[id
Analysis Batch: 14739
Anatyte
Benzene �
Ethylbenzene
Toluene
Xylenes, Total
LCS LCS
Surrogate %Recovery Qualifier
4-Bromofluorobenzene (Surr) 100
Lab Sample ID: LCSD 310-14732126-A
Matrix: Solid
Analysis Batch: 14739
Analyte
Benzene
Ethylbenzene
Toluene
Xylenes, Total
LCSD LCSD
Surrogate %Recovery Qualifer
4-Bromofluorobenzene (Surr) 98
Lab Sample ID: MB 310-14897/1-A
Matrix: Solid
Analysis Batch: 14911
Analyte
Benzene
Ethylbenzene
Toluene
Xylenes, Total
Surrogate
4-Bromofluorobenzene (Surr)
Organics (GC)
MB MB
Result Qualifier
<0.0961
<0.096 I
<0.0961
<0.288
MB MB
%Recovery QualiFer
97
RL
0.0976
0.0976
0.0976
0.293
Limits
80_120
Spike
Added
4.83
4.83
4.83
14.5
Limits
80_120
Spike
Added
4.72
4.72
4.72
14.2
Limifs
80 _ 120
RL
0.0961
0.0961
0.0961
0.288
Limits
80 _ 120
TestAmerica Job ID: 310-8660-1
SDG: 4604-00
Client Sample ID: Method Blank
Prep Type: TotallNA
Prep Batch: 14732
MDL Unit D Prepared Analyzed Dil Fac
mg/Kg OS/30/13 08:34 OS/30/13 09:51 1
mg/Kg OS/30/13 08:34 05/30/13 09:51 1
mg/Kg D5/30/13 08:34 O5/30/13 09:51 1
mg/Kg OS/3D/13 08:34 05/30/13 09:51 1
Prepared Ana/yzed Dil Fac �
05/30/13 08:34 05/30/13 09:51 1
Client Sample ID: Lab Control Sample
Prep Type: TotallNA
Prep Batch: 1473�
LCS LCS % Rec.
Result Qualifier Unit D % Rec Limits
4.828 mg/Kg 100 60 _ 120 --
4.630 mg/Kg 96 80 _ 12D
4.675 mg/Kg 97 SO _ 120
14.12 mg/Kg 97 80 _ 120
Client Sample ID: Lab Gontrol Sample Dup
Prep Type: TotaI1NA
Prep Batch: 14732
LCSD LCSD % Rec. RPD
Result Qualifier Unit D % Rec Limits RPD Limit
4.679 mg/Kg 99 80 _ 120 3 20
4.420 mg/Kg 94 80 _ 120 5 20
4.455 mg/Kg 94 80 _ 120 5 20
13.47 mg/Kg 95 80 _ 120 5 20
Page 11 of 19
MDL Unit
mg/Kg
mglKg
mg/Kg
mg/Kg
Client Sample ID: Method Blank
Prep Type: TotallNA
Prep Batch: 14897
D Prepared Analyzed Dil Fac
05l31/13 06:53 05/31/13 10:56 1
OS/31/13 08:53 05/31/13 10:56 1
OS/31/1308:53 05/31/1310:56 1
05l31/13 08:53 OS/31/13 10:56 1
Prepared Analyzed Dil Fac
05/31/13 08:53 05/31/13 i0:56 1
TestAmerica Cedar Falls
6/4/2013
'
QC Sample Results
Client: Carlson McCain, Inc. TestAmerica Job ID: 310-8660-1 '
Project/Site: 4604-00 SDG: 4604-00
Method: WI-GRO - Wisconsin - Gasoline Rar�ge Organics (GC) (Continued)
Lab Sample ID: LCS 310-14897/2-A Client Sample ID: Lab Control Sample '
Matrix: Solid Prep Type: Total/NA
Analysis Batch: 14911 Prep Batch: 14897
Spike LCS LCS % Rec. ,
Analyte Added Result Qualifier Unit D % Rec Limits
Benzene 4.60 4.881 mg/Kg 106 BO _ 120
Ethylbenzene 4.60 4.683 mg/Kg 102 80 _ 120 '
Toluene 4.60 4.747 mg/Kg 103 80 _ 120
Xylenes, Total 13.8 14.16 mg/Kg 103 80 _ 120
LCS LCS
Surrogate %Recovery Qualifer Limits •
4-Bromofluorobenzene (Surr) 96 80 _ 120
�Lab Sample ID: LCSD 310-14897125-A C{ient Sample iD: Lab Control Sample Dup �
Matrix: Solid Prep Type: Total/NA
Analysis Batch: 14911 Prep Batch: 14897
Spike LCSD LCSD % Rec. RPD
Analyte Added Result Qualifier Unit D %Rec Limits RPD Limit ,
Benzene 4.82 4.804 mg/Kg 100 80 _ 120 2 20
Ethylbenzene 4.82 4.497 mg/Kg 93 80 _ 120 4 20
Toluene 4.82 4.570 mg/Kg 95 80 _ 120 4 20 '
Xylenes, Total 14.5 13.76 mg/Kg 95 BO _ 120 3 20
LCSD LCSD
Surrogate %Recovery Quali�er Limits �
4-Bromofluorobenzene (Surr) 96 80 _ 120
Method: WI-DRO - Wisconsin - Diesel Range Qrganics (GC)
Lab Sample ID: MB 310-14692/1-A Client Sample ID: Method Blank '
iNlatrix: Solid Prep Type: Total/NA
Analysis Batch: 14629 Prep Batch: 14692 '
MB MB
Analyte Result Qualifier RL MDL Unit D Prepared Analyzed Dil Fac
Diesel Range Organics (DRO) <7.00 7.00 mg/Kg OS/29/� 3 17:51 05/30/13 23:41 1
l.ab Sample ID: LCS 310-1469212-A Client Sample ID: Lab Control Sample �
Matrix: Solid Prep Type: Total/NA
Analysis Batch: 14629 Prep Batch: 14692
Spike LCS LCS %Rec. '
Analyte Added Result Qualifier Unit D % Rec Limits _
Diesel Range Organics (DRO) 100 130.7 ` mg/Kg 131 70 _ 120
Lab Sample ID: LCSD 310-14692/3-A Client Sample ID: Lab Control Sample Dup '
Matrix: Solid Prep Type: Total/NA
Anaiysis Batch: 14629 Prep Batch: 14692
Spike LCSD LCSD % Rec. RPD '
Analyte Added Result Qualifier Unit D % Rec Limits RPD Limit
Diesel Range Organics (DRO) 100 134.4 ' mg/Kg 134 70 _ 120 3 20
'
TestAmerica Cedar Falls ,
Page 12 of 19 6/4/2013 '
Client: Carlson McCain, Inc.
ProjecUSite: 4604-00
GC VOA __
Prep Batch: 14732
Lab Sample ID
310-8660-3
LCS 310-14732/2-A
LCSD 310-14732/26-A
MB 310-14732/1-A
Analysis Batch: 14739
Lab Sample ID
310-8660-3
LCS 310-14732/2-A
LCSD 310-14732/26-A
MB 310-14732/1-A
Prep Batch: 14897
Lab Sample ID
310-8660-1
310-8660-2
LCS 310-14897/2-A
LCSD 310-14897/25-A
MB 310-14897/1-A
Analysis Batch: 14911
Lab Sample ID
310-8660-1
3I0-8660-2
LCS 310-14897/2-A
LCSD 310-14897/25-A
MB 310-14897/1-A
GC Semi VOA
Analysis Batch: 14629
Lab Sample ID
310-8660-2
LCS 310-14692/2-A
LCSD 310-14692l3-A
MB 310-14692/1-A
Prep Batch: 14692
Lab Sample ID
310-8660-1
310-8660-2
LCS 310-14692/2-A
LCSD 310-14692/3-A
MB 310-14692/1-A
Analysis Batch: 14869
Lab Sample ID
310-8660-1
Client Sample ID
MeOH Blank
Lab Control Sample
Lab Control Sample Dup
Method Blank
Client Sample ID
MeOH Blank
Lab Control Sample
Lab Control Sample Dup
Method Blank
Client Sample ID
B-1 (10')
B-2 (10') �
Lab Control Sample
Lab Control Sample Dup
Method Blank
Client Sample ID
B-1 (10') --
B-2 (10')
Lab Control Sample
Lab Control Sample Dup
Method Blank
Client Sample ID
B-2 (10')
Lab Control Sample
Lab Control Sample Dup
Method Blank
Client Sample ID
B-1 (10')
B-2 (10')
Lab Control Sample
Lab Control Sample Dup
Method Blank
Client Sample ID _
B-1 (10')
QC Association Summary
Prep Type
Total/NA
Total/NA
Total/NA
Total/NA
Prep Type
Total/NA
Total/NA
Total/NA
Total/NA
Prep Type
Total/NA
Total/NA
Total/NA
Total/NA
Total/NA
Prep Type
Total/NA
Total/NA
Total/NA
Total/NA
Total/NA
TestAmerica Job ID: 310-8660-1
SDG: 4604-00
Matrix Method Prep Batch
Soil 5035
Solid 5035
Solid 5035
Solid 5035
Matrix Method Prep Batch
Soil WI-GRO 14732
Solid WI-GRO 14732
Solid WI-GRO 14732
Solid WI-GRO 14732 :
s,
Matrix Method Prep Batch
Soil 5035
Soil 5035
Solid 5035
Solid 5035
Solid 5035
Matrix Method Prep Batch
Soil WI-GRO �489�
Soil WI-GRO 14897
Solid V�9-GRO 14897
Solid WI-GRO 14897
Solid WI-GRO 14897
Prep Type Matrix Method Prep Batch
Total/NA Soil WI-DRO 14692
Total/NA Solid WI-DRO 14692
Total/NA Solid WI-DRO 14692
Total/NA Solid WI-DRO 14692
PrepType Matrix Method _ Prep Batch
Total/NA Soil 3550B
Total/NA Soil 35506
Total/NA Solid 3550B
Total/NA Solid 3550B
Total/NA Solid 35508
Prep Type Matrix Method _ _ Prep Batch
Total/NA Soil WI-DRO 14692
Page 13 of 19
TestAmerica Cedar Falls
6/4/2013
,
Lab Chronicle
Client: Carlson McCain, inc. TestAmerica Job ID: 310-8660-1 '
ProjecUSite: 4604-00 SDG: 4604-00
Clieni Sample ID: B-1 (10') Lab 5ample ID: 310-8660-1
Date Collected: 05/24113 10:25 Matrix: Soil '
Date Received: 05/25113 09:20 Percen4 Solids: 77.3
Batch Batch Dilution Batch Prepared '
Prep Type Type Method Run Factor Number or Anaiyzed Analyst Lab
TotaI/NA Prep 5035 14897 05/31/13 08:53 CMM TAL CF
Total/NA Analysis WI-GRO 1 14911 OS/31/13 13:39 CMM TAL CF
Total/NA Prep 3550B 14692 05/29/13 17:51 ELS TAL CF ,
Total/NA Analysis WI-DRO 10 14869 06/02/13 14:17 KKD TAL CF
Client �ample ID: �-2 (10') Lab Sample ID: 310-8660-2 �
Dafe Coflected: 05I24l13 10:30 Matrix: Soil
Date Received: 05/25/13 09:20 Percent Solids: 82_5
Batch Batch Dilution Batch Prepared '
Prep Type Type Method Run Factor Number or Analyzed Analyst_ Lab
Total/NA Prep 5035 14897 OS/31/13 08:53 CMM TAL CF
Total/NA Analysis WI-GRO 1 14911 05/31/13 14:06 CMM TAL CF ,
Total/NA Prep 3550B 14692 05/29/13 17:51 ELS TAL CF
Total/NA Analysis WI-DRO 1 14629 OS/31/13 03:00 KKD TAL CF
Client Sample ID: MeOH Blank Lab Sample iD: 310-8660-3 '
Date Collecied: 05l24I13 10:35 Matrix: Sail
Daie Received: 05/25l13 09:20
Batch Batch Dilution Batch Prepared �
Prep Type Type Method Run Factor Number or Analyzed Analyst Lab
Total/NA Prep 5035 14732 OS/30/13 08:34 CMM TAL CF
Total/NA Analysis WI-GRO . 1 14739 OS/30/13 13:41 CMM TAL CF '
Laboratory References:
TAL CF = TestAmerica Cedar Falls, 704 Enterprise Drive, Cedar Falls, IA 50613, TEL (319)277-2401 '
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TestAmerica Cedar Falls ,
Page 14 of 19 6/4/2013 �
Certification Summary
Client: Carlson McCain, Inc.
ProjecUSite: 4604-00
Laboratory: TestAmerica Cedar Falls
All certifications held by this laboratory are listed. Not all certifications are applicable to this report.
Authority Program EPA Region
AIHA �H�P
Illinois NE�P 5
lowa State Program 7
Kansas NELAP 7
Minnesota NE�P 5
North Dakota State Program 8
Oregon NELAP 1�
Wsconsin State Program 5
Certification ID
101044
200024
7
E-10341
019-999-319
R-186
IA1D0001
999917270
TestAmerica Job ID: 310-8660-1
S DG: 4604-00
Expiration Date
11-01-14
11-29-13
12-01-13
01-31-14
12-31-13
09-29-13
09-29-13
08-31-13
� . -'
'- —
TestAmerica Cedar Falls
Page 15 of 19 6/4/2013
Method Summary
Client: Carlson McCain, Inc.
ProjecUSite: 4604-00
'
TestAmerica Job ID: 310-8660-1 '
SDG: 4604-00
Laboratory �
TAL CF
TAL CF
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Method Method Description Protocol
WI-GRO Wisconsin - Gasoline Range Organics (GC) WI-GRO
WI-DRO Wisconsin - Diesel Range Organics (GC) WI-DRO
Protocol References:
WI-DRO ="Modifed DRO: Method For Determining Diesel Range Organics", Wisconsin DNR, PubI-SW-141, September, 1995.
WI-GRO ="Modified GRO: Method For Determining Gasoline Range Organics", Wisconsin DNR, PubI-SW-140, September, 1995.
Laboratory References:
TAL CF = TestAmerica Cedar Falls, 704 Enterprise Drive, Cedar Falis, IA 50613, TEL (319)277-2401
Page 16 of 19
�
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,
'
TestAmerica Cedar Falls '
6/4/2013 '
�- � - — - --
���-�����-i�� TestAmerica �ample Receipt and i �i
=�����-�m��"� Cedar Falls Fa�ility i II
�{t� . �.�.�.'f• th i.::1':rtC:'::.�`.1.Iii�L'rE:i71NC�
7D4 Enlerpnse Drive • Cedar Falls, 1A 506�3 II �
rei sie-r�-zaoi � Fax 3�9•z��-zazs 310-8660 Chain cf Custody
I
\__ -- -- - ------ -
Client: �����, /�, � ��� Project: y�s - �a ----
City:
State:
Date: �� 2��i�' � Receiver's Initials: � Time (Delivered): %: �'
iemperature Record:
Cooler ID#�itaPpi;�abie>
Uncorrected Temp:�
j, �' °c
Corrected Temp:
�� � °c
Thermometer:
� I R - � 11531565 "D"
�IR - 111531506 "E"
� IR - 61854108 "Front"
� 111655718 - Probe
�Temperature blank
�Temperature out of compliance
Coolant Record:
�Received on ice
�
�Wet ice
� Blue ice
� Dry ice
�Ofher:
�NONE
Cusiody Seals:
Cooler Custody Seals Preseni?
�Yes �No
Sample Custody Seals Present?
�Yes �No
Document No.: CF-LG-WI-G02
Revision: 19
Date: 2122/2013
Courier:
�UPS �TA Courier
�FedEx �TA Field Services
�FedEx Ground �Client
�US Postal Service �Other:
' �Spee-Dee
Excepfions Noted:
�Sample(s) not received in cooler
�Sample(s) received same day of sampling
--. .. _. .. --
Evidence of chilling process
I �Temp blank <0°C, samples NOT FROZEN
�Temp blank <0°C, samples FROZEN
�Temperature not taken: �rndr�afe �ason)
�Non-Conformance Repart Started
Cooler Custody Seais intact?
�Yes �No �N/A
Sample Custody Seais Intact?
�Yes �No �N/A
Page 17 of 19
6/4/2013
'�.:�
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T���/� m��� Cry Cedar Fails Division Phone: 319 - 277 - 2401 or 1- 800 - 750 - 2401
%"'�I I! L•�� 704 Enterprise Drive Fax: 319 - 277 - 2425
Cedar Falis, IA 50613
THE LEADER IN ENVIRONMENTAI TESTING '
compar,y: Carlson McCain, I11C. Your PO #: ��L'i`7 � i�Q �
i
5end ReportTo: Citt'IS �OCiI ' Invoice To: ChrlS LoCh
aadre5s: PO L�ox 429 / 5300 Highway 55359 r,a Q�ote #: � i? ,
city/statelziP Code: Map{e Plalil, MN 55359 � Project Number: �{�d��-r��
Telephone Number:952-346-3913 FaX: 952-346-3901 Site / Location ID: �S5'/ �31{.,� �%i6%�s��rGS %ti/'ri�'�/'��i_s
Sampled by: (Print Name) G�i{�t�r� �e��� ' State: ��j✓ ^-- �i-'rOL��/
'� .
(Signature) ���^���'r� — � S
� � •Y
� � � � � � � �
� ri r � � � a� � � ■■�
Login Sample Receipt Checklist
Client: Carlson McCain, Inc.
Login Number: 8660
List Number: 1
Creator: Facciani, Melene K.
Question
Radioactivity wasn't checked or is </= backyround as measured by a
survey meter.
The cooler's custody seai, if present, is intact.
Sampie custody seals, if present, are intact.
The cooler or samples do not appear to have been compromised or
tampered with.
Samples were received on ice.
Cooler Temperature is acceptable.
Cooler Temperature is recorded.
COC is present.
COC is filled out in ink and legible.
COC is filled out with all pertinent information.
Is the Field Sampler's name present on COC?
There are no discrepancies between the containers received and the COC.
Samples are received within Holding Time.
Sample containers have legible labels.
Containers are not broken or leaking.
Sample collection date/times are provided.
Appropriate sample containers are used.
Sample bottles are completely filled.
Sample Preservation Verified.
There is sufficient voi. for all requested analyses, incl. any requested
MS/MSDs
Containers requiring zero headspace have no headspace or bubble is
<6mm (1/4").
Multiphasic sampies are not present. .
Samples do not require splitting or compositing.
Residual Chlorine Checked.
Answer
N/A
True
N/A
True
True
True
True
True
True
True
True
True
True
True
True
True
True
True
True
True
True
True
True
N/A
Comment
Job Number: 310-8660-1
SDG Number: 4604-00
List Source: TestAmerica Cedar Falis
TestAmerica Cedar Falis
Page 19 of 19 6/4/2013
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