HomeMy WebLinkAboutDERR-2024-004893SUPPLEMENTAL INFORMATION FOR NO FURTHER ACTION
Crus Oil Inc.located at 2260 South West Temple,Salt Lake City,Utah
Facility Identification 4000202,Release Site NMB &NMP
Table of Contents:
1.Internal Memorandum (add Memo
file to Closure Packet once finalized)
2.Supplemental Information
2.RBCA Tier 1 Worksheet
3.Site Map
4.Soil Analytical Results
5.Groundwater Analytical Results
6.Soil Gas Analytical Results
7.Site-Specific Cleanup Level Calculator
8.Water Rights Map
9.Groundwater Protection Zones Map
10.Topographic Map
SUPPLEMENTAL INFORMATION FOR NO FURTHER ACTION
Crus Oil Inc.located at 2260 South West Temple,Salt Lake City,Utah
Facility Identification 4000202,Release Site NMB &NMP
Facility History:
Crus Oil Inc has been a bulk oil facility since 1928.The site is currently equipped with 30
aboveground storage tanks (ASTs)containing various grades of oil,waste oil,hydraulic fluid and
transmission fluid.There is one oil/water separator located on the west side of the property;
storm drains are connected to the separator.In 1995,Intermountain Environmental Consultants
removed a 500-gallon oil UST from the northeast section of the property and the site was issued
a No Further Action letter.Two additional tanks were removed in 1997.A release was reported
in 2016 as part of a Phase II investigation.UST tanks and contaminated soil were removed in
2017.Additional Contamination was found and excavated in four different areas in 2020.
Excavation occurred down to 10 feet deep.Area was repaved.Soil vapor samples were taken sub
slab.Most contamination was found under MW-1,which is located in the center of the site under
asphalt.
There is a municipal well within 500 feet of the release however it was sampled and did not
contain contamination.Drinking water in the area comes from other municipal sources.The site
is not in a groundwater protection zone.
An Environmental Covenant has been signed by Crus Oil and the Director and recorded with the
Salt Lake County Recorder's Office.
Current Land Use:
The property is currently occupied by Crus Oil Inc,and is considered industrial.The surrounding
land use is commercial and industrial.A UTA TRAX line borders the western boundary of the
property.Groundwater depth is at 10 feet below ground surface and the soil type is organic silts
and clays,and fill.
Actions Taken to Eliminate or Control the Source of Contamination:
In May 2016,a consultant conducted four Phase II investigations and a UST removal on the
property.During demolition of the northern building in October 2017,approximately 682.61 tons
of contaminated soil was excavated.In August 2020,Additional excavation occurred in four
separate areas.Soil was excavated to a depth of 10 feet,and approximately 700 tons of
contaminated soil was removed.Approximately 2,354 gallons of groundwater was extracted and
treated.The area was backfilled and covered with asphalt.
Nature and Extent of Contamination:
Soil and groundwater contamination have been delineated to the site.Soil contamination was
found to be below Tier 1 Utah risk based corrective action (RBCA)screening levels with the
exception of TPH-DRO in CS-MW12 and TPH-ORO in CS-MW-1.Water contamination was
found to be below Tier 1 Utah risk based corrective action (RBCA) screening levels.
Contamination is found at depth around 5-10 feet. Remaining contamination is inaccessible,
controlled, or mitigated by the fact that drinking water is supplied by a municipal source and the
shallow groundwater is not used in the area.
Exposure Pathways:
Groundwater Ingestion Exposure Pathway
This pathway is complete as there is a domestic well within 500 feet of the property. However, it
was sampled and no contamination was found. This pathway will be controlled or mitigated by
the fact that drinking water is supplied by a municipal source and the groundwater plume is
present only beneath the on-site property.
Soil Leaching to Groundwater Exposure Pathway
Soil leaching to groundwater is assumed to occur at the property, due to the presence of residual
petroleum-related compounds in subsurface soil and in groundwater. This pathway will be
controlled or mitigated by the fact that drinking water is supplied by a municipal source and the
shallow groundwater is not used in the area.
Soil Leaching to Surface Water Exposure Pathway
This pathway is incomplete as there is no surface water within 500 feet of the site.
Vapor Intrusion to Indoor Air Exposure Pathway
This pathway is incomplete as demonstrated by near-slab sampling completed at MW-12, the
only sampling location with soil and groundwater contamination above Tier 1 SLs that is near a
building. The target screening level calculated for the commercial building on the adjoining
property with a 0.03 slab attenuation factor applied is 16.4 ug/m3 benzene, and the near-slab
sample result was 22 ug/m3. Other contamination remaining above Tier 1 SLs at the site is at a
depth of 10 feet and not situated under buildings. Additionally, the site is overlain with asphalt
and not accessible to the general public.
Vapor Intrusion to Outdoor Air Exposure Pathway
This pathway is incomplete because the remaining contamination is at a depth of 10 feet.
Additionally, the site is overlain with asphalt and not accessible to the public. Soil vapor
sampling found that those nearest buildings are below Site-specific target levels, and those above
(MW-1) are located under asphalt. Utilities are not within 50 feet besides the storm drains which
lead to the oil/water separator. Construction workers and others who may come into direct
contact with the contaminated soil will be notified by blue stakes before any redevelopment or
utility work begins.
Due to the nature and location of contamination that has been left in-place, the DERR is utilizing
Blue Stakes of Utah to receive notification when excavators may be digging within the
contaminated area. The DERR will provide the attached flyer to excavators when notification is
received from Blue Stakes.
Economic Considerations, Technology Available, and Cost Effectiveness of Cleanup
Options:
Additional cleanup of this site is not warranted because there are no not addressed complete
exposure pathways. Contamination is currently at a depth of 10 feet and additional excavation
would be difficult, involving excavating into the foundation of the building deeper than 10 feet
below ground surface.
Additional excavation would be cost prohibitive and undo previous work. Hot spots have been
removed and remaining contamination is overlain by buildings with no vapor intrusion risk as
evidenced by sub-slab vapor sampling. The site has overlain the contaminated soil
with asphalt.
The Department recommends that Crus Oil contamination be added to blue stakes and log its
location. An Environmental Covenant for this site restricts the land use.
Recommendation for No Further Action:
This site meets the Corrective Action Cleanup Standards Policy for UST sites at Utah UST Rule
R311-211. Further cleanup of this site is not warranted as the remaining contamination is not
likely to adversely affect human health and the environment as discussed above.
An Environmental Covenant for the site has been signed and filed with the Salt Lake County
Recorder's Office as of September 18, 2023.
Facility Information
Facility Name:CRUS OIL INC.Release ID:NMB
Facility Address:2260 S WEST TEMPLE SOUTH SALT LAKE, UT
84115
Facility ID:4000202
Notification Date:11/11/2016
Owner Name:CRUS OIL INC Reporting Party:Scott ONeill
Owner Address:PO BOX 65438 SALT LAKE CITY, UT 84165 Project Manager:Porter Henze
Site Assessment Information
a. Contaminant Source Information Cause of Release (if known)
Product
Released
Amount
Released (gal)
Size (gal) # of
USTs Tank Piping Disp Over/Spill Other Comments
Gasoline Yes Yes
Diesel Yes Yes
Waste Oil Yes Yes
Unknown
Other
Tank Piping Disp Free Prod Cont Soil
Sources Removed:Yes Yes No No Yes
b. Land Use Information
Current Land use at the Site:Industrial Surrounding Neighborhood:Commercial
(Note: Surrounding land use is Residential if one or more residences share a common property line with the Facility)
c. Soil Information Soil Type(s)
Depth to Contaminated Soil
(feet below land surface):
10 OH-Organic silts & clays 10'
Method of Soil Type Identification:Unified Soil Classification
d. Groundwater Information
Was groundwater encountered?:Yes Thickness of Free Product:
Depth to groundwater
(feet below land surface):
10 Is groundwater impacted at any
concentration:
Yes
Groundwater flow direction: Measured Slope direction of surface topography:N
e. Distance from Highest Measured Contaminated Concentrations and Sampling Location to Nearest Potential Receptor
Receptors:(Enter distance to each receptor from corresponding sampling location in feet)
Distance- Location Distance- Location
Water Line: - Sewer Line: - Building Desc:Industrial
Electrical: - Natural Gas: - Other Desc:
Building:60 - MW-1 Telephone: -
Property Line 200 - MW-1 Storm Drain: -
Other(specify): -
Receptors Within 500 feet:
Municipal Well:>500 Domestic Well:200 Irrigation Well:>500
Other:
Surface Water(specify type: lake, stream, creek, river, wetland):Dist: >500 Desc:
Utah's RBCA Tier 1 Worksheet
Printed on: 5/5/2022 1:36:29 PM
Facility History - Executive Summary
Site has long been used as a bulk oil facility. Site was slated for redevelopment and several UST and AST tanks were removed.
Contamination was found and excavated in four different areas. Excavation occurred down to 10 feet deep. Area was repaved. Soil
vapor samples were taken sub slab. Most contamination was found under MW-1, which is located in the center of the site under
asphalt.
RBCA Tier 1 Screening Level Evaluation
Groundwater(mg/L)Soil(mg/Kg)
Constituent ISL/Tier 1 Level Highest Concentration and
Sampling Location
ISL/Tier 1 Level Highest Concentration and
Sampling Location
Benzene 0.005/0.30 0.187 MW-1 0.20/0.90 0.0443 CS-MW12-NW
Toluene 1.0/3.00 .0042 MW-14 9.0/25.0 0.161 CS-MW2-NW
Ethylbenzene 0.7/4.00 0.065 MW-14 5.0/23.0 0.16 CS-MW1-WWS
Xylenes 10.0/10.0 0.104 MW-14 142.0/142.0 2.28 CS-MW2-NW
Napthalene 0.70/0.70 0.119 MW-12 51.0/51.0 25.1 CS-MW12-EW
MTBE 0.20/0.20 0.001 MW-1 0.30/0.30 0.002 CS-MW1-NW
TPH-gasoline 1.0/10.0 3.82 MW-15 150/1500 1,310 CS-MW1-WWS
TPH-diesel 1.0/10.0 4.86 MW-12 500/5000 5,080 CS-MW12-EW
Oil and Grease/TRPH 10.0/10.0 5.26 MW-1 1000/10000 142,000 CS-MW1-
NW@5
Recommended Tier 1 Actions
All contaminant concentration levels are below ISLs or below Tier 1 screening levels and no receptors are within the critical
distances. Recommendation - No further action.
Tier 1 criteria (contaminant concentration and/or distance to receptors) are exceeded at the site.
Recommendation - See attached supplemental information worksheet.
Evaluation Completed by:Date:
DERR Project Manager's Signature
Utah's RBCA Tier 1 Worksheet
Printed on: 5/5/2022 1:36:29 PM
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5/05/2022
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Sample Location Map
Figure Prepared By Date
March20223S. O'Neillfn$neerlng and Sclence, Inc.
488 E. Winchester Street, Suite 420
Murray, Utah 84107
Project Number: 16-15785 1.20
A*
A
F-;] Subject properry
i
----| Approximate Warehouse Footprint $ Monitoring Well ', Soil Gas Sampling Point
$ Abandoned May 1,2011 and October 24, 2018
PARTNER ASTs
Approximate Excavation Boundary
@ Boring Location
$ Monitoring Well to be replaced
2260 South West Temple Street
South Salt Lake, Utah 84115
Table 2: Soil Sample LatEratory Results
2260 South West Temple
South Salt Lake, Ubh 84115
Partner Prcjd Numb€. 16-157851.15
November 2020
cs-Murl2-ww
cs-Mw12-EW
cs-Mw12-B
cs-Mwl2-sw @ 9
cs-Mwtz-sw @ 5
cs-Mwl1-EWS
cs-Mwll-vt w5
cs-Mwl1-sw
cs-Mwtl-B
cs-Mw11-EWN
cs-Mwr1-wwN
cs-Mwl1-NW
cs-Mv$t-B
c5-MW-2-SW
cs-Mw2-Ew
cs-Mw2-Nw
cs-Mw2-tuw
cs-Mwt-sw
cs-Mw1-Elivs
cs-Mw1-wws
cs-Mw1-EwN
cs-Mw1-wwN
cs-Mwl-B
cs-Mwl-Nw@ 9
C5-MW1-NW @ 5
11/17/2020
11/'t7/2020
11t1712020
11/16/2020
11/16/2020
11123/2020
11/23t2020
11/23/2020
11/20/2020
't1/20/2020
11/20/2020
11/20/2020
11/25/2020
11/2s/2020
11n5/2020
11/25/2020
11/25/2020
11/17/2020
1',1117/2020
11/17/2020
11/17/2020
't1/17/2020
11t17/2020
11/16/2020
1't/16/2020
<0.041
<0.0398
<0.00234
<0.00201
<o_(xx16
<o.oo217
<0.00221
<0.00211
<0.00209
<0.001 9
<0.0021
<0.002
<o.oo224 a
<0.0021 8 J4
<0-00208 J4
<0.00206J4
<0.@22414.
<0.00211
<0.00192
<0.00202
<0.00227
<0.00204
<0.00205
<0.00195
<0.@202
<0.041
<0.0398
0.00358
<0.00201
0.00541
<0.00217
<o.00221
<0.0021 1
<000209
<o001 9
<0.0021
<0.002
0.0028
0.00849
0.m417
0.o476
0.01 85
0.0122
o0339
o0459
o.0237
0.0753
0.00308
0.032
0.0944
<0.205
<o199
<0.0117
<0.0100
<0.208
<0.0109
<0-011 1
<0.0105
<0.01(x
<0.00951
<0.o'105
<0.00999
<o.0112
0.011
<0.01 (x
0.161
0.041
<0.0105
<0.0()96
0.0155
<0.0114
0.0154
<0_01 02
<0.00975
0.0124
<0.103
0.12I
0.0145
<0_00502
<0.0104
<0.00543
<0.00554
0.0259
<o.00522
0.018
0.o112
0.00934
<0_00559
0.00877
<0.00522
0.0322
0.0265
0.00994
0.0201
0.16
0.0819
0.0674
<0-00512
0.0184
0.oot6
<0.266
<0.2s9
<0.0152
<0.01 31
<o.o27
<0.0141
<0.01,14
0.ou7
<0.0136
0.0514
0.0326
0.0139
0.024
0.316
0.186
2.28
1.98
<0.0'137
0.0215
0.178
0.0658
0.0617
<0.0133
0.0171
0.0384
<0.513
25.1
3.77
<0.0252
<0.0521
<0.0271
<0.0276
<0.0263
<o.0262
0.cr''37
0.239
<0.0249
<0.028
<o.0272
<0.026
<0-0258
<0.0281
<o.0264
<o.o24
<0.0254
<0-0284
0.15
<0.0256
<0.0244
<0.0252
161
46
48.7
<s.02
<5-21
317
139
757
<522
669
129
276
<5.59
253
,160
33
390 Jt
166
669
1,310
1,05r,
185
9.U
189
521
1,370
5,O8t J7
61
2,420
591
2,930
620
340
<5.1
1,950
1,920
2,390
<526
793
97.2
1,140
1380.17
97.5
103
1,120
1,g(xt
204
<5.1
't27
239
< 128
651
< 136
1,870
522
2,920
605
2,5&
128
1290
1,550
1.890
<'131
940
612
9,950
3,330
<126
<124
208
243
123
l,rllO
5,970
142,000
ETEXMN via EPA Merhod 3260, TPH-GRO via EPA Melhod 801 5, nd TPH-DRO via EPA Method 3545.
and Oil and Gr€a5e via EPA Method 9071 S (nrg/k9)
Sample lD Date
MTBE Eenzene Toluene TPH-GRO TFH-DRO oil & Gron'e
TotalEthvlbenzene Nrohthilene' Xylenes '
mg/kg = milligrams perkilogEm
BTqMN = BeuencTolu€ne EttvlbeEen€, Xyleftr Methytted-bu!/ether naphftatene
TPH-GRO = total pdrcleum hydrc66ons gasolinerange organic
TPH-DRO = total pdrol€um hydrceftons di*l Gng€ oEanics
EPA = Unitd States Envircnmenbl Prordion Agenq
Utah lsb = Utah lnitialscrening bds (November2&5)
RBCA = Rkk Basd CorcdkAdion
< = not detedd rbove indicatd l.boEtory Repodd Oetdion Limit (RDL)
J1 = Surogare r*ov€ryljmib have been €xcftdd; vatues arcodside upf @ntoilimiE
,4 = The assodatd batch QC Ms outside the gtabtkhd qu.tity codol Enge for accuEry
J7 = sunogate.eovery.annot b€ usd forcontrct limitflatuation dueto dituiion
B = fre sahe analyt€ k found in the assocbtd blank
Valu€s in bld and highlightd yelow dcd RBCA Tier 1 screning bd
Table 2: Soil Sample Laboratory Results
2250 South West Temple
South Salt Lake, Utah 841 1 5
Partner Project Number 16-157851..16
November 2020
cs-Mw16-ww
G5-MW15-WW@ s
cs-Mw16-sw
cs-Mwl5-sw@ 5
cs-Mw16-EW
cs-Mwt6-Ew @ 5
cs-Mwl6-B
cs-Mwl6-NWE
cs-Mwl6-NWW
cs-Mwt2-Nw
1',t/19/2020
11/19/2020
11/19/2020
11t19/2020
11/19/2020
11/19/2020
11/18/2020
11/16/?O2O
11/16/2020
11/17/2020
<0.00218 J4
<0.00239 J4
<o.o0221 J4
<0.00211 t4
<0.00206
<0.@,248 )4
<0.@216 J4
<0.002 1 5
<0.00208
<0.(M43
<0.00218
<0.00239
<002?1
<0.0021 1
<0.00206
<0.0021t{}
<0.00216
<0.00215
<0.00208
<0.0443
<0.0109
<0_01 19
<0.011 1
<0.0106
0.0333
o.0227
<0.0108
<0.0107
<0.01 04
<o.222
0.00593
<0.00597
0.0132
0.0119
0.0162
o.o171
<0.0054
0.0135
<0.0052',l
<0.1 t1
0.0886
<0.0155
0.458
o.544
2.O1
1.U
<0.014
0.689
<0.0135
<0.288
<o-o273
<0.0298
<0.0277
<0.0265
<0.0258
<0.031
<0.027
<0.0269
0.138
<0.555
252
<5-97
482
166
204
152
<5-4
t65
<5-21
39rl
260
111
1,060
2820 J2
3,130
669
<5.2
t,990
s.71
s,t20
+120
417
3,150
c630
7,760
2,7il
388
6,O70
't67
807
BTEXMN via EPA Method 8260, TPH-GRO via EPA Method 8015, nd TPH-DRO via EPA Method 3546,
and Oil and Grease via EPA Method 9071 B (mglkg)
Toluene Ethylbenzene Naphthalene TPH-GRO TPH-DRO Oil & Grease' Xylenes
Sample lD Date
MTBE Benzene
Total
5'l
51o.2
0.3
o.2
0.9
9.0
25
5
23
Utah lSLs
RBCA Tier 1 Screeninq Level
142
142
150
1,500
500
5,000
1,000
10,000
Notes:
mg/kg = milligrams per kilogram
BTEXMN = BeEene, Toluene, EthylbeEenq Xylenet Methyl tert-butyl dher, naphthalere
TPH-GRO = total p€troleum hydrocarbons gasoline 6nge organics
TPH-DRO = total petroleufr lydrocarbons disel range organics
EPA = United States Environmental Protfttion Agency
Utah lSLs = utah Initial Screning Ldels (November 2005)
RBCA = Risk Basd Corrective Action
< = not deteded above indicated laboratory Repoded Detedion Limit (RDL)
J2 = Surogate r*overy limits have been exceded; values are ou8ide lwer control limitg
i4 = The e$ablished batch QC was outside the dablished quality range.
J6 = The sample matrix interfered with the ability to make any accurate detemination; spike value is low.
Pl = RPD value not applicable forsample concentrations less than 5 tim6 the reporting limil
Table 2: Soil Gas Sample VOCs Laboratory Results
2260 South West Temple
South Salt Lake, Utah 84115
Partner Project Number 1 6-1 57 851.20
March 16,2022
SG-MW-15
sG-MW-12
SG-MW-11
SG-MW-2
sG-MW-1
<19
<91
<18
<25
<10,000
22
22
25
39
5,qto
27
12,000
31
65
<20,000
6.2
4n
6.6
76
<10,000
15
2,100
22
110
< 10,000
8-0
1,100
9.3
41
< 10,000
< 5.3
<27
<5.3
<5.3
<z,(XrO
<25
<120
<25
<25
<200,000
Notes:
VOCs = volatile organic compounds
EPA = United States Environmental Protection Agency
Vg/m3 = micrograms per cubic meter
OLEM = Office of Land and Emergency Management
Tracer Gas = lsopropyl alchohol
TCR = Target Canceer Rate
HQ = Hazard Quotient
NA = not applicable
Values in bold exceed laboratory RLs
Yellow highlighted values exceed residential regulatory guideline
PARTNER
Table 3: Soil Gas Sample TPH Fractionation Laboratory Results
2260 South West Temple
Murray, Utah 84115
Pa rtner Project N u m ber 1,6-!57 851,.20
March '1,6,2022
EPA OIEM Target Subslab Soil Gas
Concentration OCR = 10'6 HQ - 1)
EPA OttM Target Subslab Soil Gas
Concentration OCR = lOs HQ' 1)
EPA OLEM Target Subslab Soil Gas
€oncentration (TCR ' 10{ HQ = 1}
sG-MW-16
sG-MW-12
sG-MW-11
sG-MW-2
SG-MW-1
960
16,000
1_700
5,400
NA
87,6{X'
87,600
87,600
NA
NA
NA
NA
10,000,000
8?,600
87,600
87,6(x!
220
< 1,000
580
< 1,000
NA
82500
87,600
87,600
620
< 1,000
910
3,800
NA
14600
14,600
14,600
120
< 1,000
170
1,300
NA
VOCs via 82608
(pglm3)
TPHv (c6) TPHv (C7-C8)
Aliphatics Aliphatics
Sample ldentification TPHv (C6-C10)*
EPA Method
Units
TPHv (C5-C8)
Aliphatic
TPHv (C9-C10)
Aliphatics
Notes:
TPH = Total Petroleum Hydrocarbons
EPA = United States Environmental Protection Agency
pg/m3 = micrograms per cubic meter
* = Total TPH
NA = Not Analyzed
OLEM = Office of Land and Emergency Management
Tracer Gas = lsopropyl alchohol
TCR = Target Cancer Rate
HQ = Hazard Quotient
< = not detected above indicated laboratory Reporting Detection Limit (RDL)
NE = not established
Values in bold exceed laboratory RDLs
Orange highlighted values exceed residential and commercial/industrial regulatory guidelines
Page 1 of 3
SSCL Calculator Prepared for:SSCL Calculator Prepared by:
Site name:
Site address:
Facility ID:
Release ID:
Contact name:
Contact phone:
Contact e-mail:
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Benzene (71-43-2)c 1.64E+01 22 MW-1 9.87E-03 1.69E-01 1.47E+02 5.20E+00 4.18E-03 7.56E-01 6.33E+00
Toluene (108-88-3)nc 2.44E+05 12000 MW-1 8.18E+00 2.68E+03 2.46E+06 7.50E+03 9.09E+01 1.64E+04 5.44E+03
Ethylbenzene (100-41-4)nc 4.94E+04 490 MW-1 1.02E+01 5.79E+02 5.46E+05 1.72E+04 2.96E+01 5.34E+03 6.72E+03
Xylenes (1330-20-7)nc 4.94E+03 2100 MW-1 2.04E+01 5.47E+01 4.85E+04 3.54E+04 4.13E+00 7.46E+02 1.07E+04
Naphthalene (91-20-3)nc 1.46E+02 27 MW-1 2.04E+00 7.91E+00 2.77E+03 4.47E+03 2.98E+00 5.39E+02 1.32E+03
MTBE (1634-04-04)nc 1.46E+05 91 MW-1 5.11E-01 3.55E+03 7.37E+05 1.21E+02 1.74E+02 3.14E+04 3.41E+02
Alkyl benzenes (C9-C10)
[average values]nc 1.02E+04 1300 MW-1 4.09E+00 1.25E+02 1.17E+05 1.40E+04 1.33E+01 2.39E+03 2.66E+03
Alkyl naphthalenes (C11-C13)
[average values]nc 3.07E+02 4.09E+00 5.18E+02 1.85E+05 6.86E+04 1.48E+03 2.68E+05 1.75E+04
Total PAHs (C12-C22)
[average values]nc 1.53E+02 3.07E+00 4.13E+01 2.89E+04 4.54E+05 5.44E+02 9.82E+04 1.21E+04
Aliphatics (C5-C6)
[Hexane (110-54-3)]nc 1.02E+04 10000000 MW-1 6.13E+00 9.62E+01 1.03E+05 1.70E+05 7.71E-01 1.39E+02 3.93E+03
Aliphatics (C7-C8)
[Heptane (142-82-5)]nc 1.02E+04 3800 MW-1 6.13E+00 1.16E+02 1.24E+05 3.47E+05 1.07E+00 1.94E+02 3.93E+03
Aliphatics (C9-C10)
[Nonane (111-84-2)]nc 1.48E+03 1300 MW-1 1.02E+01 6.57E+02 7.02E+05 1.80E+06 8.07E+00 1.46E+03 6.72E+03
Aliphatics (C11-C12)
[Undecane (1120-21-4)]nc 1.48E+03 1.02E+01 7.46E+02 7.98E+05 8.62E+06 5.41E+01 9.78E+03 6.72E+03
Aliphatics (C13-C16)
[Hexadecane (544-76-3)]nc 1.48E+03 1.02E+01 8.61E+02 9.21E+05 1.21E+08 8.85E+02 1.60E+05 6.72E+03
Aliphatics (C17-C21)
[Heptadecane (629-78-7)]nc 1.02E+04 2.04E+02 7.11E+03 7.60E+06 1.92E+11 8.48E+05 1.53E+08 1.35E+05
Aliphatics (C22-C35)
[Heptadecane (629-78-7)]nc 1.02E+04 2.04E+02 7.11E+03 7.60E+06 1.92E+11 8.48E+05 1.53E+08 1.35E+05
Date prepared:10/22/2015
version 1.2 updated 10-22-15
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
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Name:
Company, Agency, other:
Phone:
E-mail:
UST Consultant Cert. #:
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)
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Crus oil sscl Page 1 of 3
5/16/2022
10:02 AM
5/5/22, 1:11 PM Map
https://maps.waterrights.utah.gov/EsriMap/map.asp#1/1
Water Rights Map
Point (1) Location: Address: 2260 S WEST TEMPLE ST, SALT LAKE CITY
0 100 200ft
N
S
W E
Pr inted from the Utah DEQ In ter active Map
5/13/2 022 1:18,056
0 0.2 5 0.50.1 25 mi
0 0.45 0.90.225 km
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7
QUADRANGLE LOCATION
SALT LAKE CITY SOUTH QUADRANGLEUTAH - SALT LAKE COUNTY7.5-MINUTE SERIES
U.S. DEPARTMENT OF THE INTERIOR U.S. GEOLOGICAL SURVEY
This map was produced to conform with the National Geospatial Program US Topo Product Standard, 2011.A metadata file associated with this product is draft version 0.6.18
CONTOUR INTERVAL 5 FEETNORTH AMERICAN VERTICAL DATUM OF 1988
SCALE 1:24 000
1000 500 0 METERS 1000 2000
21KILOMETERS00.51
1 0.5 0
MILES
1
1000 0 1000 2000 3000 4000 5000 6000 7000 8000 9000 10000
FEET
×
ÙGN
MN
0°37´11 MILS
11°16´200 MILS
UTM GRID AND 2019 MAGNETIC NORTHDECLINATION AT CENTER OF SHEET
4500VL
VK
Grid Zone Designation12T
U.S. National Grid100,000 - m Square ID
UTAH
1 Baileys Lake
8 Draper
2 Salt Lake City North3 Fort Douglas4 Magna5 Sugar House6 Copperton7 Midvale
ADJOINING QUADRANGLES
2
54
3
7
1
86
Imagery.....................................................NAIP, June 2016 - October 2016Roads......................................... U.S. Census Bureau, 2016Names............................................................................GNIS, 1979 - 2019Hydrography...............................National Hydrography Dataset, 2002Contours............................................National Elevation Dataset, 2009 - 2016Boundaries..............Multiple sources; see metadata file 2017 - 2018Public Land Survey System................................................BLM, 2019Wetlands.................FWS National Wetlands Inventory 1997 - 1998
North American Datum of 1983 (NAD83)World Geodetic System of 1984 (WGS84). Projection and1 000-meter grid:Universal Transverse Mercator, Zone 12T
Produced by the United States Geological Survey
This map is not a legal document. Boundaries may begeneralized for this map scale. Private lands within governmentreservations may not be shown. Obtain permission beforeentering private lands.
SALT LAKE CITY SOUTH, UT
2020
Expressway Local Connector
ROAD CLASSIFICATION
Ramp 4WD
Secondary Hwy Local Road
Interstate Route State RouteUS RouteWX./H
*7
6
4
3
0
1
6
4
0
0
1
3
4
*
NS
N
.
7
6
4
3
0
1
6
4
0
0
1
3
4
NG
A
R
E
F
N
O
.
U
S
G
S
X
2
4
K
3
9
5
1
2
Sitex